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6. Discussion
6.1 The conservation impact of scientific research
The levels of implementation reported in this study (57%) are remarkably similar to the
figures reported by Flashpohler et al (2000) and Ormerod et al (2002) of 57% and 54%
respectively. These estimates had previously been
considered over-optimistic, particularly
with reference to the low figures of institutional uptake of research findings reported by Pullin
et al (2004) and Sutherland et al (2004) However, whilst it is likely that researchers would
over-report rather than under-report the use of their findings, 60% of the ‘yes’ responses were
qualified by relatively detailed further comments (Box 1). It should be emphasised that Pullin
et al (2004) incorporated only the use of the actual literature, not the possibility that the
research had been disseminated and
incorporated in other forms, and more positive figures
have been reported for species action plans in the US (Boersma et al, 2001; Clark et al, 2002).
Interestingly, the levels of implementation were highest when the corresponding author was
from Australasia, similar to the findings of Pullin & Knight (2005), suggesting that there are
certain areas in which conservation managers are more amenable to the use of scientific
literature.
It is also worth noting that the figures reported here constitute responses from only 33% of the
appropriate literature included in the initial sample. This figure could therefore incorporate
some element of respondent bias towards those whose findings had been implemented, rather
than self reporting. However, validation of the author and research
characteristics with a
sample of non-respondent papers showed attributes to be similar (section 4.8).
It could be suggested that the 47 % of findings implemented in practical conservation action
(table 2) rather than policy (table 3) is a more accurate figure, but there is justification for
including these responses as a ‘yes’ in the majority of the analysis, as the findings taken up are
being used to develop species action plans and policy, or by specialist groups such as the
IUCN. Even if this is
not immediate practical action, studies have suggested that this has
practical use (Fuller et al, 2003; Boersma et al, 2001; Lunquist et al, 2002)
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It is perhaps a sign of the scale of the issues surrounding conservation science that, given the
current state of biodiversity (Bini et al, 2005) and taking into account that the research
examined was from five of the major conservation journals over a six year period, a roughly
50% level of implementation could be seen as optimistic. These journals provide the main
forum for the best
quality conservation research, on which it is widely agreed that
conservation actions should be based (Smallwood et al, 2000). Equally disturbing is that this
figure has not increased since the studies by Ormerod et al (2002) and Flashpohler et al
(2000), despite the increasing recognition of the need for better links between researchers and
practitioners (Meffe, 1998; Fazey et al, 2004; Prendergast et al, 1999; Underwood, 1995;
Pullin et al, 2004; Sutherland et al, 2004). It is also entirely possible that the research findings
played less of a role in implementation
that the authors are aware, and indeed 15% thought
that it had played only a minor role.
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