Category Archives: Macroecology

Pollinator biodiversity and why it’s important: a new review just published – download it for free

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In a new review paper that’s just been published in the Annual Review of Ecology, Evolution and Systematics I have looked at the question of just how diverse the pollinators are, and why pollinator biodiversity is ecologically important and therefore worthy of conservation.  I’ve taken a deep time and wide space approach to this, starting with what the fossil record tells us about when animal pollination evolved and the types of organisms that acted as pollinators in the past (the answer may surprise you if you’re unfamiliar with the recent paleontological literature on this topic).  Some of the most prominent biogeographical patterns have been highlighted, and I have tried to estimate the global diversity of currently known pollinators.  A conclusion is that as many as 1 in 10 described animal species may act as pollen vectors.

As well as this descriptive part of the review I’ve summarised some recent literature on why pollinator diversity matters, and how losing that diversity can affect fruit and seed set in natural and agricultural contexts.  Extinction of pollinator species locally, regionally, and globally should concern us all.

Although I was initially a little worried that the review was too broad and unfocused, having re-read it I’m pleased that I decided to approach the topic in this way.  The research literature, public policy, and conservation efforts are currently moving at such a fast pace that I think it’s a good time to pause and look at the bigger picture of what “Saving the Pollinators” actually means and why it’s so important.  I hope you agree and I’d be happy to receive feedback.

You can download a PDF of the review entitled Pollinator Diversity: Distribution, Ecological Function, and Conservation by following that link.

Pollination ecologists should also note that in this same volume of Annual Review of Ecology, Evolution and Systematics there’s a review by Spencer Barrett and Lawrence Harder called The Ecology of Mating and Its Evolutionary Consequences in Seed Plants.  If you contact those authors I’m sure they’d let you have a copy.

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Filed under Apocynaceae, Bees, Biodiversity, Biogeography, Birds, Butterflies, Climate change, Ecosystem services, Evolution, Honey bees, Hoverflies, IPBES, Macroecology, Mammals, Moths, Mutualism, Neonicotinoids, Pollination, Urban biodiversity, Wasps

Saved by a bee: a true story, with reflections and photos from PopBio2017

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The blog has been a bit quiet of late, due to a lot of traveling on my part, starting with field work in Tenerife, then a weekend away with friends on the Isle of Wight, followed by the topic of this post: PopBio2017 – the 30th Conference of the Plant Population Biology Section of the Ecological Society of Germany, Austria and Switzerland in Halle, Germany.  And I’d like to begin with a story….

The organisers of PopBio2017 had invited me to be one of five keynote speakers at the conference and I was due to deliver a talk on “The macroecology of wind and animal pollination” first thing (09:00) on Thursday morning.  So the night before I duly set my phone’s alarm for 07:00, thinking I’d have enough time to get ready, have breakfast, then take the tram to the venue (a 15 minute ride/walk).

It was a very hot night and I left the windows open, but my mind was restless with thoughts of how to deliver the talk most effectively.  So I kept waking up during the night, and actually slept through the alarm.  The next thing I know it is 07:45 and I am being woken up by an urgent buzzing noise….from a bee!

I swear this is true: a bee had flown in through the window, buzzed for a few seconds right in front of my face, and woke me up in time to deliver my talk on pollinators!  It then turned around and flew straight back out of the window.

It actually wasn’t until I’d jumped out of bed and into the shower that I’d woken up sufficiently to appreciate what had happened…and wondered if anyone would actually believe me!  Anyway, I got to the venue with 15 minutes to spare, the talk seemed to go well, and it’s a story I think I’ll enjoy telling for some time to come.

The conference was really fabulous, with some very impressive science on show.  It was a good mix of postdocs, PhD students, and established researchers talking on a diverse range of plant ecology topics, not just “plant population biology” (whatever that really is – there was some discussion on that score).   The organisers had arranged the programme so that the keynotes in each session were followed by shorter talks broadly related to that topic, so I was followed by a series of presentations on pollination biology.  And very good they were too.

Here’s some photos from the week:

A slightly blurry audience waiting for my talk to begin (not as blurry as me after the dash to the venue however…):

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I was fascinated by the coypu that are common in the River Salle which flows through the city of Halle.  They are classed as an invasive species, but are very, very cute:

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Indeed so cute I couldn’t resist taking a selfie…

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Some interesting urban greenery including swales for flood defence:

 

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Wall plants surviving the graffiti:

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Halle’s most famous resident, Handel:

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There’s a Harry Potter feel to some parts of the town:

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The fabulous double-double-spired cathedral:

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There had to be a spiral or two, of course:

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On the Saturday after the talks had finished we took an excursion to the fascinating “Porphyry Hills” dry grasslands – unique western extensions of plant communities and species normally found in the east, including many plants of the steppe:

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These rocky outcrops have become exposed as agricultural ploughing caused the surrounding soil level to drop:

 

Some of the grassland areas have very thin soils with resultant high plant diversity:

 

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Lots in flower, though not as many pollinators as I would have liked:

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On the last evening a couple of us had a private tour of the university’s botanic garden, and well worth a visit it is too:

It was a thirsty conference – “To beer or not to beer….”?

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Finally thanks to the organisers of PopBio2017 for the invitation to speak, and to all of the conference attendees who made it such a special meeting.

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Filed under Bees, Biodiversity, Gardens, Macroecology, Pollination, spirals, Urban biodiversity

The macroecology of animal versus wind pollination – a new study just published

In collaboration with colleagues in Brazil, Denmark, and elsewhere in the UK, we’ve just published a new research paper which looks at the global spatial distribution of wind and animal pollinated plant species, and the underlying historical and contemporary ecological causes of that distribution.  It’s a study that builds on my “How many flowering plants are animal pollinated?” paper in Oikos, and has been a long time in its gestation.  We’re very excited by its findings and plan to develop this project in the future.

As a bonus we made the cover of the journal with the amazing image below!  Big thanks to Pedro Viana and Jesper Sonne for the photos.

Here’s the citation with a link to the publisher’s website; the abstract is below.  If anyone wants a PDF copy, please ask.

Rech AR, Dalsgaard B, Sandel B, Sonne J, Svenning J-C, Holmes N & Ollerton J (2016) The macroecology of animal versus wind pollination: ecological factors are more important than historical climate stability. Plant Ecology & Diversity 9: 253-262

 

Abstract:

Background: The relative frequency of wind- and animal-pollinated plants are non-randomly distributed across the globe and numerous hypotheses have been raised for the greater occurrence of wind pollination in some habitats and towards higher latitudes. To date, however, there has been no comprehensive global investigation of these hypotheses.

Aims: Investigating a range of hypotheses for the role of biotic and abiotic factors as determinants of the global variation in animal vs. wind pollination.

Methods: We analysed 67 plant communities ranging from 70º north to 34º south. For these we determined habitat type, species richness, insularity, topographic heterogeneity, current climate and late-Quaternary climate change. The predictive effects of these factors on the proportion of wind- and animal-pollinated plants were tested using correlations, ordinary least squares (OLS) and logistic regression analyses with information-theoretic model selection.

Results: The proportion of animal-pollinated plant species was positively associated with plant species richness and current temperature. Furthermore, in forest, animal pollination was positively related to precipitation. Historical climate was only weakly and idiosyncratically correlated with animal pollination.

Conclusion: Results were consistent with the hypothesised reduced chance for wind-transported pollen reaching conspecific flowers in species-rich communities, fewer constraints on nectar production in warm and wet habitats, and reduced relative effectiveness of wind dispersal in humid areas. There was little evidence of a legacy of historical climate change affecting these patterns.

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Pollinators and pollination – something for the weekend #9

The latest in an (ir)regular series of posts to biodiversity-related* items that have caught my attention during the past few weeks; this one’s focused on pollinators and pollination because there’s been so much emerging on this recently it’s been impossible to decide what to write more fully about!

 

Feel free to recommend links that have caught your eye.

*Disclaimer: may sometimes contain non-biodiversity-related items.

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Tropical Zombies: Moles & Ollerton (2016) is now published

P1080615Back in March 2014 I reported about a guest blog that Angela Moles (University of New South Wales) and I had written for the Dynamic Ecology blog entitled “Are species interactions stronger and more specialized in the tropics?”  The post generated a lot of comments, not all of them supportive of what we were saying.  It also resulted in an invitation from the editor of the journal Biotropica to write up the post as a commentary.  This we did and duly submitted, it went through a couple of rounds of peer review, and has now finally been published.

The paper is currently open access on the Biotropica website as an early view item; here’s the reference hyperlinked to it:

Moles, A. & Ollerton, J. (2016) Is the notion that species interactions are stronger and more specialized in the tropics a zombie idea? Biotropica DOI: 10.1111/btp.12281 

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Extinction of British bees and flower-visiting wasps – a new assessment of rates and causes

Extinction of species is perhaps the most fundamental assault that we as humans can inflict on the rest of the natural world.  Extinctions take a range of forms, from the loss of a whole species (such as the sad case of the St Helena Giant Earwig, recently declared extinct by the IUCN), down to extirpation of local populations.

For an island nation such as Britain, extinctions at a country level are highly significant because there is limited opportunity for species to disperse across the sea and re-colonise areas where they previously lived.  In a new research paper published this week in the journal Science we have addressed the subject of pollinator declines in the UK and asked the following questions:

1.  How many bee and flower-visiting wasp species have gone extinct in the UK?

2.  Is the rate of extinction (e.g. number of species per decade) constant or variable over time?

3.  Can we interpret any patterns in relation to broader societal changes, for example in agricultural policy, conservation strategies, etc?

The research is a collaboration between myself and University of Northampton colleagues Dr Robin Crockett and Dr Hilary Erenler, together with Mike Edwards from the Bees, Wasps & Ants Recording Society (BWARS), the c. 500,000 records of which were used in these analyses.  This is probably the most extensive data set on these insects available for any country and an important resource.

The answer to the first question is that 23 species of bees and flower-visiting wasps have gone extinct, ranging in time from the crabronid wasp Lestica clypeata (last observed in 1853) to the solitary bee Andrena lathyri (not seen since 1990).  All of these species still occur on mainland Europe, so these were country-level extinctions, not species extinctions.

The answer to questions 2 and 3 is that the rate of extinction is highly variable, and by using a novel statistical approach adapted by Robin to analyse the changing rate over time, we found that the main period of species loss followed changes to agricultural policy and practice just after the First World War.  This is much earlier than previously believed: until now it has usually been the Second World War and the subsequent Common Agricultural Policy which have been seen as the main drivers of pollinator loss.  This figure produced by Robin shows the results in detail:

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The four periods marked in red are the points where we estimate the rate of extinction changed (with 99% confidence intervals shown in pink).  The most rapid rate of extinction (shown by the solid blue piecewise regression lines and dashed 99% confidence intervals) is from the late 1920s to the late 1950s.  This, we believe, is the cumulative effect of agricultural changes precipitated and then augmented by the First and the Second World Wars, respectively.

The period of extinction from the late 19th into the early 20th centuries was probably caused by increased import of South American guano as soil fertilizer which increased grass productivity at the expense of wild flower diversity.  This reduced reliance on strict rotational cropping, including fallow periods with nectar- and pollen-rich weeds, and N-fixing legume years.  However it was the invention of the Haber Process in 1909, allowing industrial manufacture of inorganic nitrogen fertilizers for the first time, that fundamentally affected British agriculture.

The slow down of the rate of extinction from the early 1960s to the mid 1980s is not easily explained given the continued intensification of farming, encouraged by Common Agricultural Policy subsidies.  It could be due to the most sensitive species having been already lost, or because of conservation initiatives including the establishment of more nature reserves by organisations such as the Wildlife Trusts and the RSPB, habitat restoration and management by groups such as the British Trust for Conservation Volunteers, more farmers going organic, etc.  Or it could be a combination of both, and/or factors we’ve not yet thought of.

The final period of extinctions from 1986 to 1994, where the rate seems to increase, could be seen as evidence against the slowing in the rate of decline of pollinators in north west Europe found by Carvalheiro et al. (2013).  However  we need to be cautious here as there’s a large confidence interval around the calculated extinction rate.  The four extinctions between 1988-1990 could be an isolated cluster, or the start of a further period of relatively high extinction rate.  Only time will tell!

Bees, wasps and other pollinating insects are absolutely vital to the functioning of our natural ecosystems and for a great many agricultural crops.  We’ve known for some time that these insects are declining in Britain but now we can see how historical agricultural changes have caused species to become extinct. The big question is whether these extinctions have stopped or whether they will continue in the future. The species that have been lost to Britain still survive on the Continent and there is the possibility of natural re-colonisation or artificial reintroduction, both of which have occurred in recent years.  However in order for this to be successful we must restore as much natural habitat as possible within our farmland, which after all covers some 70% of the British land surface.  The irony of our findings, of course, is that pollinators are vital for agriculture, as the UK Government’s National Pollinator Strategy recognises.

Studies such as this illustrates the importance of maintaining the year-on-year effort of recording natural history data – the research simply wouldn’t have been possible without the BWARS records, which are mainly collected by amateur naturalists.

The full citation for the paper is:  Ollerton, J., Erenler, H., Edwards, M. & Crockett, R. (2014) Extinctions of aculeate pollinators in Britain and the role of large-scale agricultural changes. Science 346:1360-1362.  I’m happy to send a PDF to anyone who requests a copy for personal use. 

Notes:

1.  We define “extinction” as ≥ 20 years since the last recorded occurrence of the species in Britain, which is why the data stop at 1994.

2.  We have excluded single early records of species that cannot be verified as representing stable breeding populations.

3. Analyses were performed using the ‘segmented’ library in R (www.r-project.org)

4.  Thanks to Robin Crockett for the figure and the analyses, and Hilary Erenler and Mike Edwards for their input into the study.

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7 minutes is a long time in science, 7 goals is a big win in football (BES Macroecology meeting day 2)

Grey heron in Nottingham

Day 1 of the British Ecological Society Macroecology Special Interest Group ended with a drinks reception, kindly bankrolled by the International Biogeography Society, and a stark choice: dinner in a pub with good food and no television on which to watch the Brazil v Germany World Cup semi-final; or dinner in a pub with crappy food but a television.

The split amongst meeting delegates was about 50-50.  As I get older I’m being drawn to things in which I previously had only a passing interest, amongst them bird watching and football.  So I opted for the latter, and was one of only two Brazil supporters in the whole pub, the other being our guest speaker Cathy Graham, largely because we both have more Brazilian than German friends and colleagues. We were rewarded with one of the most excruciatingly clinical dissections of a major international football team that I’ve ever witnessed.  And the food was indeed crappy, but the lager was cold and plentiful.

The next morning, impelled by an uncomfortable mattress on a steel-framed bed in one of the student halls of residence, I woke early enough to do a little bird watching around the University of Nottingham’s Park Campus, which is not unlike the University of Northampton’s Park Campus, except much larger.  There was a modest diversity of birds flying and calling, the highlight being a large grey heron patrolling the edge of a circular pond.  As there were no fish in the pond it seemed to be mainly eating the slugs crawling on the adjacent lawn.  Not a behaviour I’ve ever seen before, though this year’s BBC Springwatch showed footage of parent tawny owls bringing back large slugs for their chick, so perhaps it’s more common than we realise.

Following a mediocre breakfast and disgusting coffee, it was time for the first lecture of the day, the second keynote by Cathy Graham.  Once again she focussed on her hummingbird research and presented some fascinating unpublished data on the structure of bird assemblages along an altitudinal gradient in Ecuador.  Cathy’s team has been using cheap digital cameras which take one frame a second to amass data on infrequently visited rainforest flowers, an approach that trades off time and space: it’s possible to get a long set of data, but for only a limited number of plant species and individuals.

After coffee there were papers by Katie Leach on her PhD work on competition between co-occurring species of Lagomorpha (rabbits, hares, pikas, etc.) and from Richard Field on altitudinal effects on the endemism of plants which chimed with my experiences in Tenerife.  Both of these neatly demonstrated one of the strengths of macroecology: the 21st Century tools it can marshal to use secondary data for understanding ecological patterns and processes at very large spatial scales.

But secondary data can also be a weakness of the field if the quality is poor and it is limited in scope.  This was the subject later in the day of a polemical lecture by Shai Meiri entitled “Laziness in macroecology: a crime and no punishment” that railed against researchers who sometimes fail to augment ready-made data sets with even the most rudimentary of additional data.  My favourite of Shai’s examples was a study which had used a mammalian ecology data set in which the diet of anteaters was coded as “unknown”!  The tee-shirt Shai wore during his often very funny rant read: “If you are not outraged, you were not paying attention” and there was plenty for the audience to feel outraged about, not least his suggestion that we “ban taxonomy” and (even more controversially) get away from our computer screens and into the libraries to source information to fill in the gaps in data sets.

I’d go further and say that some field work would not go amiss as well!  In comparison with using ever more sophisticated analyses, developing better software, and building ever more complex models, collecting field data seems to be low on the list of priorities for many macroecologists, particularly some of the PhD students. Not all of them by any means, and hopefully Cathy Graham’s talks will have inspired them to get into the field, but it strikes me as a trend.  That’s worrying on many levels, and good data are hard won, but then I’m an old-fashioned, muddy boots kind of ecologist who realises that our knowledge of biodiversity is built up from a very small set of data in comparison to what we don’t know: we’ve scratched the surface of the tip of the iceberg as a colleague used to say.

In the afternoon there was an unscheduled talk by Olivia Norfolk on the biodiversity of plants and pollinators of Bedouin gardens in the mountains of Sinai, which included a lot of field data.  This was followed by a second set of seven minute “lightning talks”.  I was third on a diverse bill, sandwiched within research on amphibians, Tyrannosaurus rex, North American lizards and microbial communities.  Seven minutes passes quickly and I overran slightly, but hopefully managed to convey the gist of our work on the relative frequency of wind versus animal pollination across the globe.  No one threw missiles at least and there were a couple of good questions that probed the scope and limitations of the current data, but were nowhere near as challenging as the questions in Copenhagen (though I’d had much more time for that lecture).

Following a hasty set of goodbyes I headed to Nottingham station to catch the 1810 back home, once again via the desolation of Birmingham New Street.  Reflecting on the meeting on the way to Northampton I was struck by the fact that of the forty-odd attending, I was the oldest delegate by some margin, which was even more sobering than Brazil’s loss to Germany.  I consoled myself with a bit of “train spotting” (identifying as many bird species as possible through the windows of the train), and ended up with a respectable 21 species* during the two hours or so of travel.

Thanks to the organising committee of the BES Macroecology SIG, and especially to Adam Algar and his team in Nottingham, for a great meeting.  I look forward to next year’s in Copenhagen.

 

*Blackbird, buzzard, swift, house martin, tufted duck, mute swan, mallard, jay, goldfinch, collared dove, wood pigeon, feral pigeon, starling, crow, magpie, grey heron, Canada goose, common tern, back-headed gull, common gull, pheasant, (22 if you count chickens in a run).

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Travelling west to go north (BES Macroecology meeting day 1)

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Birmingham New Street, with its subterranean platforms accessed by narrow concrete gullets, must be one of the ugliest and most unpleasant major railway stations in Britain.  It’s also, thanks to the redevelopment work currently being carried out, one of the most confusing for the traveller who only occasionally passes through.  Ugly and unpleasant I can handle if it functions well: but ugly and unpleasant AND confusing is not good.  It’s a huge contrast to Milton Keynes station which I went through last week on the way to Chester, where the open, airy platforms look out onto embankments covered in wild flowers (see the photo above).  While waiting for the train at Milton Keynes I spotted butterflies and bees visiting flowers only feet from passing high-speed engines.

As I start this post I’m sitting on Platform 9A at Birmingham waiting for a train at 0949 to Nottingham where I’m attending the British Ecological Society’s Macroecology Special Interest Group’s annual conference.  In fact I should be on the train which left platform 12A at 0919, but trying to find the unsignposted 12A, followed by a detour to pick up a coffee, meant that I missed the train by about a minute.  Not to worry, gives me an opportunity to rant about Birmingham New Street station.

The BES Macroecology SIG has been established for three years and I blogged about the inaugural meeting in London back in 2012.  I missed last year’s meeting in Sheffield so thought I’d make a special effort to get to the Nottingham event this year, even though it involves heading west (to Birmingham) to travel north (to Nottingham).

Day 1 of the meeting started with the first of two keynote addresses by Catherine Graham from Stony Brook University.  Cathy focused on her work on that most charismatic of flower visitors, the hummingbirds.  In the first talk she dealt with the importance of thinking about phylogenetic scale when conducting analyses.  Lots of thought provoking ideas and a huge amount of information to digest.

As I’m speaking on the second day I could relax and listen to some interesting talks by established and early career researchers, and PhD students, most of whom have been given 7 minutes (!) to present their work.  It’s been a challenge to whittle the final part of the talk I gave in Copenhagen last week into such a short format, but we’ll see how I get on tomorrow.  Highlights of day 1 for me included Joe Bailey talking about urbanisation, climate and alien vascular plants in the UK; Nova Mieszkowska’s work on inter-tidal species; Sive Finaly on whether Madagascan tenrecs are an example of an adaptive radiation (answer = “maybe”); and Guy Harrington on studying fossils in a macroecological manner.  But really but all the talks were good and I learned something from each of them.

As I mentioned in that post back in 2012, defining “macroecology” is problematic and there are still those who see it as synonymous with biogeography.  Perhaps one difference is that biogeography has traditionally tended to focus on patterns (e.g. how species richness changes as one moves form the poles to the tropics) whereas macroecology also seeks to explain those patterns in terms of processes, using very sophisticated statistical and mapping approaches.  But even that fails to fully appreciate biogeography which has a tradition of also trying to infer processes (for example Joseph Hooker’s 19th century work on the distribution of plants included hypothetical explanations), though without the modern analytical tools that are available to the macroecologist.  It’s a debate that will no doubt go on, though perhaps it’s a sterile one.  Does it matter what we call it as long as the science is sound?

 

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From Chester to Copenhagen

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It is 6.30am on Sunday morning but I’m wide awake and can hear the hotel in which we are staying stirring into life.  Time to reflect on what has been a long and busy week, rather than the start of a long and relaxing summer holiday as some assume academics enjoy.  That’s a myth: summers for many of us are at least as busy as the main teaching part of the year, though that’s not to say we don’t teach in the summer – I have final year project students to advise, and for students who did not pass first time round there’s still re-sit exams and assignments to be undertaken.

Of course I’m not complaining and the busyness is part of the fun of my job, which includes opportunities to travel, as I’ve previously described on this blog.  Before any travelling this week, however, Monday was taken up listening to my PhD student Kat Harrold give a seminar about the progress of her research on pollinator mapping and habitat modelling in the Nene Valley Nature Improvement Area.  This was followed by an hour’s grilling from the supervisory team and an independent colleague, as we drilled down into the research and suggested ways in which Kat could improve on the already excellent work that she’s doing.  All of this is a formal part of our PhD programme and Kat aquitted herself very well indeed.

Tuesday was the start of the travelling, and was spent in Chester helping with filming for an episode of a new four-part BBC2 series provisionally called Plant Odyssey, fronted by Carol Klein, Gardener’s World presenter and Honorary Fellow of the University. The series is being produced by Oxford Scientific Films and will be broadcast in the spring.  In the following scene we were making a rose perfume based on an ancient Roman recipe from the writings of Pliny the Elder.

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Now, I know very little about how to make perfume, but I do know a bit about flower scents and how they attract pollinators, so my role was to act as both a foil for Carol’s scent experiment and to add some science to the mix.  This is not the first filming I’ve done with Carol, having also helped out with her Science in the Garden special edition of Gardener’s World a few years ago.  While looking for that last link I discovered that all three episodes of Bees, Butterflies and Blooms is also available on YouTube, which is great to see as the BBC didn’t repeat the series or produce a DVD.  I was involved in the making of episode 2, which helped to kick-start the RHS’s Perfect for Pollinators plant labelling campaign.  Television work is fun and brings science, and the scientists who do it, to a much wider audience.

Wednesday I prepared my talk for Friday’s lecture in Copenhagen (more of which later) and Thursday involved attending the University of Northampton’s annual postgraduate research conference.  This is a highlight of the year for me as it’s an opportunity to see the breadth of postgraduate research going on across the university, something that would be impossible in a larger and more research intensive institution.  I was only able to attend the first session, but that alone covered research on the research process itself; feminist cyborg literature; the legality of the World Bank’s scrutiny panel; pollinator conservation (Kat Harrold again); and the experiences of families with children who have difficulties communicating.  Questions from the audience tended to be broad and non-specialist, and all the better for that: often it’s the straightforward, naive questions which test specialist knowledge.

The rest of Thursday Karin and I packed and then travelled up to Birmingham International for an early evening flight to Denmark.  I’d been invited by my colleague Bo Dalsgaard to present a research seminar at the University of Copenhagen’s Center for Macroecology, Evolution and Climate.  Coming from a small and very diverse department, it was great to visit such a large and specialised group of researchers, though over lunch the Center’s Director Carsten Rahbek told me that a common complaint from his staff was: “Why can’t we employ more people doing what I’m going?”  Everything’s relative I suppose.

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The title of my talk was “Pattern and process in pollination at large geographic scales”, which gave an overview of some of the research I’ve published over the last decade or so, framed around the following questions:

Quite a number of people in the Center were out doing field work or were otherwise engaged so I spoke to a modest-sized audience of some 30 people: certainly not the smallest audience I’ve ever presented to – that was three people, including the two who had invited me to give the talk!

The lecture seemed to be well received and there were some stimulating questions afterwards, though also a couple of challenging ones about statistical analysis.  One of these I couldn’t answer until afterwards because I’d forgotten the details of the methods we’d used (note to self: re-read old papers before you present their findings).  In answering the other I agreed with the questioner that the data could now be analysed in a more sophisticated way (future task, if I ever get the time).  If Kat’s reading this, I hope she takes satisfaction in not being the only person to be asked difficult questions about their research this week!

Afterwards I chatted with Bo and Carsten about the limitations of the current and paleo-climate data sets we’ve been using in some studies, which are indeed very limited.  But there are only two options.  Do we work with data sets that are flawed, whilst acknowledging that any conclusions are tentative?  Or wait until better data become available, which could be a decade in the future?  My choice is definitely to go with the former, otherwise we’d never publish anything because there are always limitations to data used in studies of ecology and biodiversity. Personal and public honesty about such limitations, and ideas as to how they can be overcome in the future, are surely preferable to stalling research.

Later that afternoon I discussed science with two of Bo’s collaborators, Pietro Maruyama a Brazilian PhD student whom I’d met last November, and Peter, a Danish undergraduate.  Both are doing excellent work on that most charismatic group of pollinators, the hummingbirds.

Friday evening I was exhausted, and Karin and I opted for dinner in the hotel restaurant and an early night, as Saturday was to be spent exploring Copenhagen. It’s a great city for wandering around, with fascinating architecture and unexpected additions to buildings, such as bronze dragons:

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And parks with statues of artists and writers, such as Hans Christian Andersen:

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After a roundabout wander, via a gallery selling African tribal art (which we couldn’t afford) and a small lunch (which we could only just afford – Copenhagen’s an expensive city!) we eventually ended up at the University’s Botanical Garden, which has a superb living collection of cacti and succulents, orchids and other epiphytes, and alpine plants.

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It beautifully illustrates the huge morphological diversity encompassed within the 352,000 or so species of flowering plants, one of the many reasons why I love visiting botanical gardens: I always see something new.  This included two species of bumblebees (Bombus) which I’m sure don’t occur in Britain.  I’ll have to look them up when I get back:  from Chester to Copenhagen and, tomorrow, back to Northampton.

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Filed under Bees, Biodiversity, Biogeography, Gardens, Macroecology, Pollination, Royal Horticultural Society, University of Northampton

Guest blogging: Are species interactions stronger and more specialized in the tropics?

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In hushed tones the narrator describes the intricate details of yet another highly specialized relationship between one species of indescribable beauty and a second species with intricate behaviour that is about to eat/infect/cooperate with/exploit it [delete as appropriate].

The camera view pulls back to reveal the green cathedral of a tropical rainforest: 

“The tropics” continues the narrator “are special…….…”

 

Yes, the tropics are special.  But how special?  Or more to the point, how different are tropical communities to temperate communities?  Over at the Dynamic Ecology blog, Jeremy Fox has invited Angela Moles and myself to contribute a guest blog on the subject of whether the idea that species interactions are always stronger and more specialized in the tropics is outmoded and not backed up by the evidence.  In Jeremy’s parlance, is it a zombie idea?

The subject of latitudinal variation in species interactions is one that has interested me for a while and I’ve written a few papers on the topic, especially in relation to how plant-pollinator interactions vary with latitude.  You’ll find references to some of them in the Dynamic Ecology piece, plus a fuller over view of our arguments.

So what are you doing reading this?  Get over to Dynamic Ecology and read that!

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Filed under Biodiversity, Biogeography, Evolution, Macroecology, Mutualism, Pollination