Society for Conservation Biology: 2002 Annual Meeting
Abstracts
< Go Back
Society for Conservation Biology: 2002 Annual Meeting
|
|
Society for Conservation Biology 16th
Annual Meeting July 14-July 19 2002
co-hosted by DICE and the British Ecological Society
Abstracts for Symposium Sixteen
Toward evidence-based conservation practice:
a policy framework for co-ordinating science and practice
Keynes Lecture Theatre 1
Monday 15th July: 10.15 - 12.15
|
(BLOCK CAPITALS indicate the presenting author)
10.15 - 10.30
DOLMAN, PAUL, Centre for Evolution, Ecology & Conservation, University of
East Anglia, Norwich, NR4 7TJ, UK, <p.dolman@uea.ac.uk>
WHAT IS EVIDENCE-BASED CONSERVATION?
I show that much conservation investment lacks any evidence for its effectiveness,
and has rarely been tested against alternative approaches. Instead, conservation
activity is often based on insight, hunches, best guesses or myth. In public health
such an approach would be regarded as scandalous. Evidence-based medicine has radically
changed the manner in which doctors operate. I will review the main principles used
in evidence-based medicine and use examples to show how these principles can be applied
to testing and optimising conservation activity.
10.30 - 10.45
KNIGHT, TERI, Health Services Management Centre, The University of Birmingham,
Edgbaston, Birmingham B15 2RT UK, <t.m.knight@bham.ac.uk>
EVIDENCE-BASED PRACTICE IN MEDICINE AND PUBLIC HEALTH
The practice of medicine has relatively recently gone through an effectiveness revolution
that has improved the criteria upon which treatment strategies are based by progressing
from reliance on personal experience to reliance on scientific evidence. Evidence-based
practice is a model of proceeding in decision-making that aims to provide the best
available evidence to the decision-maker(s) on the likely outcomes of alternative
actions. The model relies on; a. addressing appropriate questions through good quality
research; b. the production of systematic reviews of the primary literature, which
evaluate the evidence (including its quality) for the effectiveness of alternative
actions in achieving stated objectives and then c. making this information available
to decision-makers. The evidence-based approach is now being applied more widely
to the sphere of public health management and policy. The model will be summarized
and the main elements discussed with reference to its application in other fields
such as conservation.
10.45 - 11.00
CÔTÉ, ISABELLE M. and Nicola Blay, School of Biological Sciences,
University of East Anglia, Norwich NR4 7TJ, UK (i.cote@uea.ac.uk)
OPTIMAL CONDITIONS FOR CAPTIVE BREEDING IN HUMBOLDT PENGUINS: AN EVIDENCE-BASED APPROACH
Holding conditions for animal populations held in captivity have evolved largely
independently across zoological institutions, and as a result are extremely variable
for any given species. To assess empirically the optimal conditions for captive breeding
of endangered Humboldt penguins (Spheniscus humboldti), we surveyed 16 British
zoos and bird gardens which exhibit this species and obtained information on population,
enclosure and husbandry characteristics, as well as per capita egg productivity,
chick productivity and hatching success. All three measures of breeding success increased
with number of breeding pairs. Chick productivity was highest when nesting boxes
were lined with sand and gravel. Hatching success increased with pool size and was
highest in enclosures with concrete floors. Adult mortality was low but appeared
related to the use of chlorine in freshwater pools and to the presence of other penguin
species in Humboldt penguin displays. These results thus yield clear recommendations
for optimising conditions for captive breeding of Humboldt penguins and, if implemented,
could reduce the extreme variation in hatching success (0 - 90%) and chick productivity
(0 - 0.55 chick bird-1 year-1) found among penguin populations. This evidence-based
approach is widely applicable to other species commonly held in captivity.
11.00 - 11.15
AUSDEN, MALCOLM., Julianne E. Evans, Mark Gurney and Graham J.M. Hirons. Royal
Society for the Protection of Birds, The Lodge, Sandy, Beds SG19 2DL. UK. <malcolm.ausden@rspb.org.uk>
CURRENT USE OF SCIENTIFIC EVIDENCE IN RESERVE MANAGEMENT
The RSPB has systems in place that can allow evidence-based conservation to take
place on its reserve network. In this paper we review the strengths and weakness
of these systems in achieving evidence-based conservation. Each reserve has a management
plan which sets out species and habitat objectives, the management intended to achieve
these objectives, and the monitoring required to determine whether these objectives
are achieved. All work carried out on the reserve is then recorded in a standardised
format on computer using the Countryside Management System (CMS). The success of
management in achieving its objectives is reviewed every five years on all reserves,
and annually at sites where large-scale habitat re-creation is taking place. A team
of ecologists interprets the information received from reserves and elsewhere, provides
advice on habitat and species management and disseminates results. It is, though,
often a major challenge to confidently interpret cause and effect of specific management
actions. This is largely because a range of techniques are often used at the same
site to achieve the same objective, and at many sites details of these techniques
vary significantly over time. It is also rarely practical to set aside large enough
areas of unmanaged land to act as controls.
11.15 - 11.30
GRANT, ALASTAIR, Philip W. Atkinson, Mark M. Rehfisch and Stephen Crooks
Centre for Ecology, Evolution and Conservation and School of Environmental Sciences,
University of East Anglia, Norwich, NR4 7TJ, UK, <A.Grant@uea.ac.uk> (AG, SC)
British Trust for Ornithology, The Nunnery, Thetford, Norfolk, IP24 2PU
EVIDENCE BASED HABITAT CREATION AND RESTORATION
Considerable effort is currently going into restoration of a wide range of habitats
but is it actually effective? We have recently reviewed the success of intertidal
habitat creation schemes for English Nature. The evidence required to evaluate their
success is often incomplete, not always of good quality and rarely published in the
peer-reviewed literature. If restoration ecology is to learn from experience we need
to ensure that monitoring programmes are properly designed, including sufficient
replication, a number of nearby natural sites if possible and non-restored sites
if appropriate. The best available methods of sampling and data analysis should be
used and monitoring programmes should be peer reviewed before and after execution.
Where a number of possible methods could be used, use several experimental treatments
within a single project is vital, as is a knowledge of the interactions between the
abiotic characteristics of sites and their ecology. Some valuable lessons can be
learned from the Norwegian experience of monitoring the impacts on marine benthos
of contamination from oil and gas platforms. Here, standardisation of sampling methodology
and a requirement to place data in the public domain have been of great assistance
in producing an overall assessment of impacts.
11.30 - 11.45
STONE, DAVE. English Nature, Northminster House, Peterborough, PE1 1UA, UK, <dave.stone@english-nature.org.uk>
NATURE CONSERVATION: THE ROLE OF PROFESSIONAL JUDGEMENT IN POLICY AND PRACTICE.
Nature conservation and the natural sciences have a long and inter-twined history.
Early 20th century nature conservation legislation in the UK was driven by empirical
data about the decline in the biological diversity of the countryside. Many developments
in land management were driven by the results of long-term research. Today, the environment
and nature conservation are subject of mainstream politics at a global scale; and
as such both policy and land management practice need to respond quickly to dynamic
socio-economic policy changes. Changes in land management practice are by policy,
by the need to exploit alternative sources of revenue, as a response to changes in
the local socio-economic climate. Empirical data is not always available to underpin
these policy and practical management decisions. The role and importance of ‘professional
judgement’ and evidence in nature conservation policy and practice decisions is examined
through case studies drawn from the UK’s implementation of the Convention on Biological
Diversity over the last 10 years. The need to capture and make better best use of
evidence will be discussed from a decision makers perspective.
11.45 - 12.00
PULLIN, ANDREW S., School of Biosciences, The University of Birmingham, Edgbaston,
Birmingham B15 2TT UK, <a.s.pullin@bham.ac.uk>
EVIDENCE-BASED PRACTICE IN CONSERVATION: BENEFITS AND CHALLENGES
Conservation increasingly involves making decisions on appropriate action from a
wide range of options. Many conservation organizations now manage species and habitats,
and produce action plans containing a diversity of objectives. Although scientific
evidence is routinely used in many cases, the majority of conservation actions remain
experience-based and rely heavily on traditional land management practices because,
although some evidence exists on which to base practice and conservationists want
to use it, much is not readily accessible in a suitable form. The model of evidence-based
practice in medicine and public health is used to explore possibilities for parallel
practice in conservation. The process of Action Plan formulation is seen as an opportunity
to encourage the evaluation of the effectiveness of conservation actions. Creating
the demand for evidence of effectiveness of alternative practices is seen as an opportunity
to improve information flow between scientists and practitioners and to encourage
formation of productive partnerships and decision support systems. Accessibility
of evidence is a key issue addressed through the need for systematic reviews and
their results being disseminated. The role of funding bodies and particularly governments
in catalysing this process is seen as key to achieving more evidence-based conservation
practice.
12.00 - 12.15
Discussion
|