A few months ago I sat down with
the aim of describing exactly what conservation science is with the hope of
producing a sort of framework. I
struggled. I struggled because, trying
to describe a science, I attempted to outline the conservation science method.
Pathology has a method and economics has a method; conservation
science (if it can be called a science) does not have a method. This is because conservation is a subject in
the same way that, for example, asking how a healthcare system could be
improved would be a subject. To improve
a healthcare system one would need not only look at biomedical research but
also how to engineer the best buildings, how to attract and train the best
staff, how to alter the public’s behaviour (in an acceptable manner) such that
the demands on the system were reduced and how to best use the available staff,
buildings and other resources. In this
blog I will explore the different strands of research which could and do
contribute to the field of conservation highlighting that, in such a complex
subject, explicitly defining the question one is answering and the framework
they are using is vitally important.
I completed my undergraduate studies
at Cambridge where, without really realising the significance at the time, I
was introduced to three academics using and investigating different, complementary
conservation methods. Head of conservation research for the RSPB, Rhys Green
lectured me on a problem solving, investigative method used to isolate the
factor causing the decline of vultures in Asia.
This was the similar approach to my idea of science, based on lab
science. William Sutherland introduced
me to horizon scanning, a method to identify the upcoming challenges for
conservation in conjunction with policy makers.
This type of research is obviously well complemented by the problem
solving approach Rhys Green expounded. William
Sutherland also introduced me to citizen science, a framework for harnessing
the information generated, often without being captured, by conservation practitioners. This framework also has the potential to complements
the Rhys Green framework, generating the data necessary to find solutions.
Andrew Balmford, in my opinion a
person who excels at providing the framework in which problems are best
considered also lectured me. Above all
else, his lectures highlighted to me the need to identify the correct currency
with which to measure the success of conservation efforts and the inevitable
trade-offs entailed. If you want to know
how successful a zoo in then you must define success, is it visitor numbers or
changes in individuals’ attitudes towards nature or the number of successful
reintroductions or profits? Are zoos
trying to maximise the same measure of success as conservation scientists? This approach largely influenced my
blog on Quality Adjusted Life Years (QUALYs), the metric used by the NHS to
quantify the value of different treatments.
It is also largely through the work of Andrew Balmford that I was
introduced to the ecosystem services approach, an attempt to find a common
currency which will allow conservation to engage with economics and politics,
the forces which, ultimately, shape human behaviour and therefore the fate of
nature (again, my blog on QUALYs examines this issue).
This last year, since graduating,
I have discovered two new methods which, I believe, have much to offer to
conservation. The first is behavioural
economics. I have stated that economics
and politics shape human behaviour but economics does not provide a perfect
prediction of human behaviour.
Understanding why individuals act ‘non-rationally’ (not as an economic
model would predict) is the realm of behavioural economics. I believe that it will prove to be extremely
valuable by aiding our understanding of the decision making of individuals,
such as farmers, whose actions determine the fate of nature. Once these decision making processes are
understood, policy makers will be able to offer farmers, and other stewards of
nature, the rewards they will respond to in exchange for actions which benefit
nature (identified via traditional research and Sutherland’s citizen science). Here
is a link to a blog I wrote on what behavioural economics can offer
conservation. The second is no so much a
method as a way of thinking (at least to me, perhaps I am not intelligent enough
to convert this new awareness into a method).
It comes from the books of Nicholas Nassim Taleb, ‘Fooled by Randomness’
and ‘The Black Swan’. These books
provide a way of thinking about randomness in complex systems, and, ultimately
conclude that it is better to be broadly right when making ecological predictions
and designing conservation interventions than attempting to make precise
predictions and being wrong. If policy
makers can be convinced that they are better served by uncertain predictions
which include a measure of the uncertainty entailed, then the conservation
would, I believe, benefit. I have also
written this
blog on this subject.
Though I have characterised the
three Cambridge professors as each pursuing different methods, in reality they
co-operate and their work overlaps greatly.
In such an interdisciplinary field, collaboration within and between
departments offers so much. I think I
will return to my blog and try to bring these strands and methods together into
some sort of framework. If you have any
comments or advice then please do leave your thoughts below. Many thanks.
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