Depression and delusion in conservation

Garnett and Lindenmayer argue that like Cassandra of Greek mythology, "foretellers of doom alone will always be ignored until too late"

By  Luke P. Shoo

Conservation biology is generally regarded as a crisis discipline (Soulé 1985). However, consensus on the nature of the discipline does not extend to how the science should be communicated in order to further the primary goal of conserving biodiversity.  Garnett and Lindenmayer (2011) contend that relentless communication of an impending mass extinction may actually be counterproductive for conservation and cite evidence from other disciplines (medicine, public health and road safety) that  bad news needs to be balanced by empowerment if political and social change is to be achieved. In a counterpoint, Arlettaz et al. (2011) argue that a focus on good news could be highly detrimental, engendering a lack of perspective and giving academics and politicians the illusion that the crisis could be solved without questioning business-as-usual practices.

An ongoing debate

This debate, played out in the journal Trends in Ecology and Evolution, has not occurred in isolation. Similar exchanges have featured in related journals including Conservation Biology (Beever 2000; Orr 2004; Webb 2005; Knight 2007; Nugent 2007; Orr 2007), Bioscience (Swaisgood and Sheppard 2010; Patten and Smith-Patten 2011; Swaisgood and Sheppard 2011) and probably elsewhere. It appears, then, that there is a fine line to be negotiated when broadcasting conservation news. We may want to combat conservation despair (Swaisgood and Sheppard 2010) but at the same time avoid the perverse outcome of breeding self-deceitand naive optimism (Noss 1995; Webb 2005).

Arlettaz et al. say that focusing on "good news" through fear of the Cassandra syndrome may be just as detrimental

‘Good news’ conservation

Some practitioners have noticed that many good news stories have failed to attract wide attention and in response have begun the task of amassing and actively communicating examples of conservation successes. In a recent example, Sodhi et al. (in press) provide a global review of conservation interventions that have likely reduced extinction and endangerment of vertebrates and environmentally damaging practices of corporations. For instance, establishment of protected areas has reduced carbon emissions from deforestation in the Brazilian Amazon and better enforcement of whaling regulations has prompted a population recovery of Pacific grey whales (Eschrichtius robustus).

Reframing the question

Much of the argument against the presentation of good news is based on the negative ramifications of cultivating blissful ignorance. However, it could well be argued that “the problem lies with ignorance, not with optimism, because ignorant pessimism is as problematic as ignorant optimism” (Beever 2000). Clearly, then, there is a role for evidence based conservation (Sutherland, Pullin et al. 2004). Moreover, there is a need to give heed to context when communicating evidence of success.

One way to do this is to  ask the question: how different would the world look in the absence of conservation action (Ferraro and Pattanayak 2006)? For example, Hoffmann et al. (2010) estimate that conservation actions have reduced the rate of deterioration in the status of the world’s animals by at least one-fifth (i.e. conservation impact). Nevertheless, almost one-fifth of all living species remain classified as threatened and on average 52 species will move one category closer to extinction each year (i.e. context) (Hoffmann, Hilton-Taylor et al. 2010).

The impacts of conservation efforts should be communicated within the correct context. Adapted from Rodrigues et al. 2006 http://www.sciencemag.org/content/313/5790/1051.full

Undoubtedly, the effects of some actions will be difficult to measure (Brooks, Wright et al. 2009). There may also be surprises that prompt us to rethink the merits of some conservation practices (Bottrill, Walsh et al. 2011). The point is that studies designed to properly evaluate the efficacy of conservation interventions can provide the raw material to report on conservation success in proper context with the ongoing reality of problem. Presenting a more complete picture may help readers resist any tendency to become environmental Pollyannas* whilst guard against conservation apathy that can stem from a mental diet composed exclusively of bad news.

*an excessively or blindly optimistic person as used by Noss (1995).

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Tips and tricks for ArcGIS, Excel and R

Liz Law reports on the Wilson Conservation Ecology Lab meeting for Aug 5th 2011

Why? Because it’s a Bustard! (Photo of Australian Bustard near Morven, QLD, by Liz Law)

How many times have we spend a good few hours (even days) trying to do something in ArcGIS/Excel only to find out, after we finished, that we could have done it in a fraction of time another way?

For me, this has occurred quite a lot. So, I decided to run our weekly lab meeting on tips, tools and functions that can save us time. Here is a quick summary of what we talked about:

Model builder and other geoprocessing tools

Making data with interpolation

Editing shapefile layers

Getting help with ESRI stuff

VLOOKUP

SDMTools

Model builder and other tools: It took me ages to find out that you can add custom toolboxes, in which you can drag in copies of your favourite tools, and also create your own using model builder.

I think model builder is a really useful tool within ArcGIS toolbox. Essentially it is a space where you can build and visualise geoprocessing models (i.e. a series of tools, functions, scripts, etc.). I find it really useful to record, communicate, and repeat your model (analysis process). I also find it a little more intuitive to batch process, or to run several processes using the output of the prior one as the input of the next (without collecting masses of intermediate files). More information on model builder is available on the ESRI website, and they also provide a free online training seminar.

Luis Verde noted that large models can get a bit buggy and can give a generic error message. When this happens, he recommends using the “make feature layer” to make a temporary copy of your inputs prior to each tool. For some reason this works.

There are also lots of geoprocessing models that already exist for a number of different tasks. Some of these can be found and downloaded at the ESRI “geoprocessing model and script tool gallery”. Other packages of tools operate as plug-ins, for example ET Geowizards, and Hawths tools (aka GME). Ayesha Tulloch says some of these are great: for example, the ET Geowizards “Explode multipart polygon” tool is way less buggy than the one provided by ArcGIS (and actually does the job right the first time). However, Ayesha also cautions that while the old Hawths tools was pretty awesome, the newer version (GME) is not. It doesn’t even work with any ArcGIS prior to 10.0, which is funny, because a lot of the functions that we use to use it for are apparently available in 10.0 anyway…

Making data with interpolation:  Jane MacDonald has not been working much with ArcGIS, but her co-workers have. And she is worried about an emerging trend to use interpolation to make data layers from point observations. While it is really easy to get results using this technique, the basic principles of models apply: junk in = junk out. You really need to question whether you are getting accurate maps, for example by validating using reserved point data, and/or comparing with GLM outputs.

Editing shapefile layers: Karen Mustin has been going through the joys of editing shapefiles. There are about a billion ways to do editing things in ArcGIS. I recommend checking out the ESRI online training seminars of which there are about 4 ones on “editing tips and tricks”. In particular, if you don’t know what “snapping” and “sticky move tolerance” are, or how to modify them, I highly recommend you seek advice BEFORE editing your layers.

Getting help with ESRI stuff: If you have spent ages trying to understand ArcGIS, gone through all the normal help and forums, and you still have unanswered questions, you can always give ESRI a call. However, many large institutions have people that are designated ESRI gateways, says Jude Keyes. Our UQ people are Jürgen Overheu (GPEM), Gai Trewinnard-McNeill (ITS), and Steven Clark (ITS).

Vlookup: Excel is probably one of the most commonly used spreadsheet programs, but probably one of the most poorly utilised ones as well. Many people turn to proper database software (and for good reason) if they have large databases that they have to run many query variations on, but you can also create a database in Excel, or do pretty basic query-like tasks. For example, Angela Guerrero suggests if you have a lookup table that you want to use to append values to a list you can use functions like VLOOKUP. If you don’t know what this is, look it up!

SDMTools: Saving the best till last, Luke Shoo blew us out of the water with his “SDMTools”. This R-package, developed by Luke and his colleagues, provides a set of tools for post processing the outcomes of species distribution models: comparing models, tracking changes in distributions over time, visualising outcomes, selecting thresholds, calculating measures of accuracy and landscape fragmentation statistics, and more. Absolutely amazing, extremely useful, and supremely beautiful.

Thanks everyone for a fantastic and very useful meeting!

Resolving the ‘Environmentalist’s Paradox’, and the role of ecologists in advancing economic thinking

- Megan Evans

Cross posted on ConservationBytes.com

Aldo Leopold famously described the curse of an ecological education as “to be the doctor who sees the marks of death in a community that believes itself well and does not want to be told otherwise”.

© T. Toles

Ecologists do have a tendency for making dire warnings for the future, but for anyone concerned about the myriad of problems currently facing the Earth — climate change, an ongoing wave of species extinctions and impending peak oil, phosphate, water , (everything?) crises – the continued ignorance or ridicule of such warnings can be a frustrating experience. Environmental degradation and ecological overshoot isn’t just about losing cute plants and animals, given the widespread acceptance that long term human wellbeing ultimately rests on the ability for the Earth to supply us with ecosystem services.

In light of this doom and gloom, things were shaken up a bit late last year when an article1 published in Bioscience pointed out that in spite of declines in the majority of ecosystem services considered essential to human wellbeing by The Millenium Ecosystem Assessment (MA), aggregate human wellbeing (as measured by the Human Development Index) has risen continuously over the last 50 years. Ciara Raudsepp-Hearne and the co-authors of the study suggested that these conflicting trends presented an ‘environmentalist’s paradox’ of sorts – do we really depend on nature to the extent that ecologists have led everyone to believe?

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Wilson Lab Journal Club: Paying for Environmental Services from Agricultural lands

- Andrea Fullagar

I was recently involved in exploring a range of possible actions for reducing biodiversity loss in Australia to include in a submission to the Biodiversity 100 campaign. One of the actions that we discussed (but which was not included in the final set published in the Guardian) was to secure a proportion of native remnant vegetation on all agricultural properties, as well as provide financial rewards to farmers who implemented management actions that were directly linked to conservation.


Agricultural land comprises 473 million hectares or nearly 62 percent of the Australian continent, so there is a clear need to engage with private landholders in order to achieve conservation outcomes across large parts of the country. As the potential to secure more protected areas diminishes, the need to implement sustainable management practices on private land becomes more pressing. Providing economic incentives to landholders in response to a direct management action would place environmental services on the market, while contributing to biodiversity conservation. Financial incentives may come in the form of subsidies or through a market-based system where payments may be administered on a competitive basis.

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