Damn the torpedoes!

My family is probably one of the few that still receives the morning newspaper delivered to the front door. My winter morning ritual consists of braving the cold for a couple of seconds to bring in the paper and then settling down to read it at breakfast with a hot cup of tea. For some reason – likely masochistic tendencies; perhaps also because it gets my brain going – I always first turn to the editorial and letters section.

Yesterday, I was presented with this letter to the editor, and I’ll admit that it got me a bit riled up. The basic premise of the letter seems to be that contemporary conservation efforts are misguided because they seek to manage crises rather than just simply “letting nature take its course.”

Here is a relevant snippet from the letter:

As the numbers of these endangered species increase it will cause a rapid decline in their food supply ending in the long, slow death by starvation. This is also going to happen to the seal populations of the Atlantic as the environmental movement demands the removal of their major predator man [sic].

There have been 90 million species that have inhabited this planet, 99 per cent have become extinct, pushed out of existence by newer more complex, more adaptable species. This process is now seen as being unnatural and declaring every species that nature is pushing into extinction must be labeled endangered and saved even if it requires the destruction of those more complex, more adaptable species for doing what nature intended them to do.

It’s hard to know where to start with this, as there are a number of problems (including a misunderstanding of evolutionary theory and history which I won’t bother to touch on here) even within that small block of text.

Many, if not most, conservation efforts these days revolve around species and ecosystems that are highly impacted by humans. In fact, it is difficult to go anywhere on earth anymore without being able to quickly find evidence of human impact. Some people have begun to call the current geological epoch the Anthropocene in recognition of the fact that human activity is leaving an indelible mark on our planet that will be detectable for eons to come. As such, many, if not most, species in crisis are in that situation due to ongoing and systemic causes such as habitat loss, pollution, or overhunting – not because they are being supplanted by “complex, more adaptable species.” This means that even the most wildly successful conservation programs rarely accomplish a return to previous levels of species numbers, let alone burgeoning population levels that lead to mass starvation. In most cases, conservationists are working within much-reduced species geographical ranges and in degraded habitats. The reduced size of the remaining land base and the deteriorated habitat are not usually capable of sustaining previous population levels.

So, let’s talk seals, since the letter writer brought them up. “Man” is, indeed, currently a major predator. But until recently humans were not capable of killing them in numbers substantial enough to have any real impact on their populations. That has all changed, of course. The fact of the matter is that humans have been the cause of the decline and demise of many, many sea mammals through combinations of hunting, overfishing of prey, or pollution. Our exploitation of these animals needs to be regulated, not simply allowed to continue carte blanche. (Note that I am not opposed to hunting – even seal hunting – but such activity needs careful monitoring.) Since seals, and many other sea mammals, reside near the top of their respective food chains, small perturbations at those levels can cause cascading effects to other levels.

Sea otters are a great example of what can happen if we do not regulate our activities. These cute sea mammals were hunted to near extinction during the fur trade over much of the Pacific coast. Sea otters eat lots of sea urchins. Sea urchins eat lots of kelp. Extremely low numbers of otters mean high numbers of urchins and much reduced levels of kelp. The heavily urchin-grazed areas that result are called urchin barrens and are obviously radically transformed from their normal state.

Thus we humans, novel predators for sea otters in terms of evolutionary time, end up having rapid and dramatic effects that reverberate deep into the ecosystem and end up returning to bite us back. In this case urchin barrens become non-productive zones for fisheries or other activities that humans value. The only way back to some semblance of normalcy (in the absence of the return of healthy populations of sea otters or other urchin predators) would be expensive and labor-intensive work that is not feasible across vast stretches of territory – e.g. removing urchins by hand.

The reality is that conservation programs require a great deal of thought, research, and often back-breaking effort. Beyond that, such programs also require consultation not just regarding the ecology and other biological aspects of the situation, but also in terms an often-tangled complex of cultural, economic, and social parameters. This is because humans are now an integral part of virtually every single ecosystem on earth, and humans are highly invested in the natural world around them, whether they realize that or not.

When we see situations of one species supplanting another, as the letter writer alludes to, there is an off chance that it is a “natural” occurrence. But more often than not it is due to choices that we are making or have made in the past. Many such situations are due, for instance, to species from other geographical regions being transplanted into a new region by humans. Not all exotic species find a foothold, but when they do the consequences can be enormous. Ask anyone in the southern USA about kudzu.

One could argue, as the letter writer seems to be doing, that we should throw up our hands and sit back and let outcomes be the outcomes across our planet. “Damn the torpedoes!”

But, while our impact on nature is massive, we also rely on the natural world to sustain us – from the air we breath to the water we drink to the food we eat.

In the end, it’s hard to fault the public for not fully understanding the intricacy and massive effort behind conservation efforts. When we see letters like this that are obviously wrong on a number of levels, at least part of the fault lies with those of us who should be communicating with the public. But letters or articles like the one that I read with my morning tea yesterday also require responding to errors in a public fashion, which is what I hope that I have at least partially accomplished here.

Feel free to add your thoughts in the comments or elsewhere. There are many other things that I could have said, and I hope that my discussion here has been accurate. I look forward to hearing what others have to say.

Spider Monday

To help to celebrate Spider Monday, here are a few spider-related papers from the archives of the Journal of Entomological Society of British Columbia.

Bennett, R.G. 2001. Spiders (Araneae) and araneology in British Columbia. J. Entomol. Soc. Brit. Columbia 98:83-90.

A fantastic survey of everything spider in British Columbia. My favorite paragraph:

Large areas and many specific habitats of BC remain uncollected and no doubt many list additions are still to come, especially from northern areas and the deep south of Be. No effort has been made to produce a comprehensive, habitat-specific spider inventory for any area in BC. That new records can be made with relative ease is suggested by the following examples: hundreds of specimens of a gnaphosid previously only known from a couple of  Washington specimens turned up in a simple pitfall study in Burnaby (see cover of Journal of the Entomological Society of BC, Vol. 96, 1999), the first specimen of a new family record for Canada came from the carpet of a provincial government office (Bennett and Brumwell 1996), and a new species record for BC came from the bathtub of an Osoyoos motel (Bennett unpublished data) in 2001.

Bennett also quotes himself, writing in another excellent article that can be found here at the Biological Survey of Canada:

…spiders are ruthless storm troops in the matriarchal anarchy that is the arthropod  world: theirs is the most diverse, female-dominated, entirely predatory order on the face of  the earth. As such, spiders are key components of all ecosystems in which they live.

 

And, since I already linked to the 1999 spider cover, above, I should also link to a couple of others from the covers of the 2004 and 1993 issues.

 

Speaking of new records, there is this paper on a new spider family record in Canada:

Bennett, R.G. and Brumwell, L.J. 1996. Zora hespera in British Columbia: a new spider family record for Canada (Araneae: Zoridae). J. Entomol. Soc. Brit. Columbia 93:105-109.

That article also contains some helpful drawings of spider genitalia. In case you didn’t know, arachnologists and entomologists are into that kind of thing.

 

Of course, the only way that we’re ever going to know what lives in remote locales is to go and visit those places ourselves. Nothing beats boots on the ground. This paper covers just that type of work, surveying spiders in a part of the world that very few of us will ever see:

Slowik, J. 2006. A survey of the spiders (Arachnida, Araneae) of Chichagof Island, Alaska, USA. J. Entomol. Soc. Brit. Columbia 103:61-70.

 

Here is an addition to a checklist of the spiders of British Columbia. The addition points back to a previous revised checklist from 1984 that we have yet to get online in the JESBC archives. Here is the addition:

West, R.C., Dondale, C.D., Ring. R.A. 1988. Additions to the revised checklist of the spiders (Araneae) of British Columbia. J. Entomol. Soc. Brit. Columbia 85:77-86.

 

Species checklists (and regular updates) are vital for understanding biodiversity and monitoring shifts in diversity over time. Along with that, it is important to get down to the natural history of the individual species on those checklists. Each species is, in itself, several careers-worth of work… at least. This type of work is arguably even more important when human influences (e.g. agriculture) are present. Here is a paper that outlines the emergence times of a variety of arthropods, including a mixture of spider species, in pear orchards:

Horton, D.R. 2004. Phenology of emergence from artificial overwintering shelters by some predatory arthropods common in pear orchards of the Pacific Northwest. J. Entomol. Soc. Brit. Columbia 101:101-108.

 

Humans (and other factors) do indeed have massive effects on biodiversity. Unfortunately we often only notice those effects when we start to see the decline in the numbers of one species or another. This, of course, assumes that we are even taking notice of some of these small creatures that are so prevalent, but often so hidden from our literal or metaphoric view. This occasional paper published by the Entomological Society of British Columbia offers an extensive coverage of likely-or-actually-at-risk spineless animals in this province that often escape notice, but which provide many of the so-called “ecosystem services” that we all rely upon. There is a long list of spiders, starting on page 10:

Scudder, G.G.E.  1994. An annotated systematic list of the potentially rare and endangered freshwater and terrestrial invertebrates in British Columbia. Occasional Paper 2.

Have a happy Spider Monday, and be sure to say hi to one of our eight-legged friends if you happen to come across one.

It’s cold out there!

Most of us would find it pretty hard to live outside all winter anywhere in Canada, let alone in places where temperatures routinely dip below -30ºC. But this is exactly what the mountain pine beetle (and many other insects) does. The question is, of course, how does it pull this off? What is it about mountain pine beetle larval physiology that allows the insects to make it through long months of deep cold?

A paper by Tiffany Bonnett and others, that recently came out of our lab, probes this process in pine beetles in a way that has not been done before. The publication is entitled “Global and comparative proteomic profiling of overwintering and developing mountain pine beetle, Dendroctonus ponderosae (Coleoptera: Curculionidae), larvae” and is available as an open access publication. We have also published the raw genomics data online at figshare. You can find those data here, here, and here.

 

What did we do?

Larval mountain pine beetles were collected from trees near to Valemount, BC during the early autumn and late autumn, and then again during the early spring and late spring. The larval beetles were prepared in the lab so that we could use a process called iTRAQ to assess all of the proteins present in the larvae at each of the different collection time points. Essentially we took four snapshots – two in the autumn and two in the spring – an then compared them to each other see what was changing. This gave us a huge amount of data to work with and we used statistics to tell us which proteins increased or decreased in prevalence across either the autumn or the spring.

 

What did we find?

Among other things:

  • Larvae expend a fair amount of energy on detoxification of host resin compounds, both in preparation for the winter, and then during feeding after winter is over.
  • Stress physiology plays a large role in this entire process, particularly in the autumn as the larvae are dealing with host tree resin toxins and readying themselves for the upcoming onset of winter.
  • We saw evidence for the involvement of several compounds that may play an antifreeze role.
  • There is an evident shift between emphasizing overwintering preparations (in the autumn) and emphasizing completing development (in the spring), consistent with expected shifting priorities at different points in the life cycle.

 

Why is this novel?

The overwintering larvae of the mountain pine beetle remain nestled under the protective bark of their host tree. This makes them quite difficult to work with, and until now not very much information had been generated on this life stage, particularly in the context of winter survival. This work, which has harnessed the power of some very useful genomics databases, has cracked the door (or the bark?) open to allow us to see in broad sweeping terms what is going on in this insect during this vital time in its life cycle. We have seen aspects of larval mountain pine beetle physiology that have never been seen before, and that provides the power to ask new questions and to investigate key genes and pathways in a much more directed manner.

 

Why is this important?

Up until now, the main known winter survival mechanism for larval mountain pine beetles was the accumulation of glycerol in the autumn. Glycerol acts as a natural antifreeze and is part of the overwintering survival tool kit of many insects. But in most known cases, glycerol is not the only part of the equation, and we didn’t think that it was the sole story in mountain pine beetle either. And it turns out that we were correct with that guess – there are a lot of other things going on as well.

In a larger sense, this means that we now have targets to focus on as we work to understand how deep winter cold can impact populations. Overwintering mortality is one of the major factors contributing to control of bark beetle populations. Now that the mountain pine beetle is moving from the cold interior of British Columbia into even-colder central Alberta, a major research question relates to the climate in its expanding geographical range and how that is going to affect the insect’s potential spread to other regions. Overlay that question with the impacts of climate change, and it should be apparent that understanding mountain pine beetle overwintering physiology is becoming more and more vital.

 

Where do we go from here?

We now have numerous potential gene targets to look at, any of which is a project unto itself. Because we have shown in other work that larval mountain pine beetles in the late summer are feeding on potentially very toxic food, we are interested in finding out how larval ability to detoxify and digest their food in the autumn can make or break their chances for winter survival. We suspect that certain larvae are better adapted than others at dealing with the nutritional challenges that they face, and thus better able to produce antifreeze compounds and the other components that allow overwintering success.

In other words, we suspect that there is variation in the mountain pine beetle population that results in some larvae surviving the winter while others don’t. We, along with collaborators, hope to determine which genes are important in this process and how selection pressure in their historical and expanding ranges are changing mountain pine beetle populations.

Some of our key questions are:

  • How do specific proteins function in protecting larvae from the cold?
  • What happens if we “knock out” some of those proteins?
  • What characteristics of tree defense and nutrition make some host trees more or less likely to allow the resident larvae to survive a winter?
  • Do adult beetle parents choose trees based in any way on how their young may fare?
  • Where in the genome should we expect to see natural selection as the insects move into colder and more inhospitable regions? How will these evolutionary shifts be observed in changes in behavior and physiology?
  • What are the larger implications of climate change on these processes?

As you can see – and as is the case with science in general – this paper not only provides some answers, but also provides fertile ground for more questions. This work, and other related work in our larger mountain pine beetle system genomics project, has given us the means to chase down some of the answers. We are looking forward to the interesting work ahead. Since this publication and its associated data are all open access, we also look forward to seeing what other people might find to do with our data.

ResearchBlogging.org
Tiffany R. Bonnett, Jeanne A. Robert, Caitlin Pitt, Jordie D. Fraser, Christopher I. Keeling, Jörg Bohlmann, Dezene P.W. Huber (2012). Global and comparative proteomic profiling of overwintering and developing mountain pine beetle, Dendroctonus ponderosae (Coleoptera: Curculionidae), larvae Insect Biochemistry and Molecular Biology DOI: 10.1016/j.ibmb.2012.08.003

Canada (finally) notices neonicotinoids

Many of you have probably heard that neonicotinoid pesticides seem to be responsible for negative effects on various pollinators, including bumblebees and honey bees.

With limited time today (and for this entire week), I won’t add much more than that right now, other than to say that others have written a ton about it already. So check out some of the links that I’ve provided for some background information.

But, I do have a reason for this brief blog post. It turns out that the Canadian government, via the Health Canada Pest Management Regulatory Agency (PMRA) are starting to take some notice and have issued a notice of intent to begin consultations on this subject. The notice of intent gives 90 days for interested parties to comment.

Some quotes from the notice of intent:

…in spring 2013 with more typical weather patterns, we continued to receive a significant number of pollinator mortality reports from both corn and soybean growing regions of Ontario and Quebec, as well as Manitoba. Consequently, we have concluded that current agricultural practices related to the use of neonicotinoid treated corn and soybean seed are not sustainable.

Bee health is a complex issue that goes beyond the incidents in 2012 and 2013 and may involve a number of additional factors, including parasites, disease and climate. Health Canada’s PMRA is currently conducting a re-evaluation of all uses of neonicotinoid insecticides in cooperation with the United States Environmental Protection Agency (US EPA) as part of the work being done with international partners. We are expediting this re-evaluation, which will help us better understand and manage potential risks these pesticides may pose to long-term bee health.

A few things to keep in mind:

  • Although the notice of intent seems to mainly target dust-related problems – and pesticide-laced dust is definitely an issue – it’s not the only issue.
  • Neonicotinoids are systemic pesticides. That means that they end up in the plant’s tissues. This is why they are very effective against herbivores (and why they were touted as such a great thing) because they are mainly targeted at things that are eating plant tissues. But the pesticide also ends up in the pollen and nectar, and that is what bees and other pollinators forage on.
  • On that topic, it’s not just honey bees that are affected. Bumblebees, as noted above, are also known to be vulnerable. In addition there are many other native pollinators – bees and otherwise – that are likely to be affected (and honey bees are not native pollinators in North America).
  • Many other organisms and ecosystems may be harmed by this class of pesticides, including fish, birds, non-pollinating insects, and soil microorganisms. This article is a decent synopsis.

It’s good to see something resembling traction on this issue emerging here in Canada.

If anyone feels so inclined, the notice of intent contains instructions for making a statement on the continued use of neonicotinoids in Canada.

 

Caterpillar stroke?

Well, it’s certainly not a butterfly stroke. But it works pretty well.

Click here to see a forest tent caterpillar swimming like a champ.