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Marine Policy
journal homepage: www.elsevier.com/locate/marpol
Strengthening post-hoc analysis of community-based fisheries management
through the social-ecological systems framework
Jessica Blythe
a,b,
⁎
, Philippa Cohen
a,b
, Hampus Eriksson
a,c
, Joshua Cinner
b
, Delvene Boso
a
,
Anne-Maree Schwarz
a
, Neil Andrew
a,c
a
WorldFish, P.O. Box 438, Honiara, Solomon Islands
b
Australian Research Council Centre of Excellence for Coral Reef Studies, James Cook University, Townsville, QLD 4811, Australia
c
Australian National Centre for Ocean Resources and Security (ANCORS), University of Wollongong, Wollongong, NSW, Australia
ABSTRACT
Community-based fisheries management (CBFM) is held up as one of the most promising approaches for securing
sustainable small-scale fisheries. Yet, the complex features that shape CBFM outcomes remain inadequately
understood. In part, this stems from the fact that few community-based projects meet the data requirements for
formal impact evaluations. Given this context, diagnostic approaches are increasingly seen as a frontier for
strengthening CBFM analysis and securing small-scale fisheries sustainability. This study explores the capacity of
Elinor Ostrom's social-ecological systems (SES) framework to strengthen post-hoc diagnosis of CBFM. It draws on
data from published and grey literature (including field notes, meeting minutes, and project reports) generated
throughout an eight-year CBFM project in five Solomon Island villages. Results suggest that successful CBFM
outcomes were facilitated by effective information sharing, harvesting rules that merge traditional and
contemporary practices, strong leadership, and resource monitoring, while uneven power differentials under-
mined positive outcomes. The paper argues that the SES framework can add analytical rigour to post-hoc
analysis when it used to: 1) engage with temporal dynamics that shape CBFM processes; 2) integrate insights
from plural theories, and 3) explore interactions between multiple CBFM outcomes. Ultimately, the paper argues
that diagnostic applications of the SES framework can contribute towards conducting more systematic analysis
of diverse CBFM data, improving CBRM practices, and realizing more sustainable small-scale fisheries
1. Introduction
Community-based fisheries management (CBFM) emerged in the
1980s as an alternative to government-led or private protection
approaches to marine resource management [1–4]. CBFM is character-
ized by the devolution of resource management authority to local
communities, allowing fisheries governance processes to be determined
locally and often involving community partnership with stakeholders
including government agencies and non-governmental organizations
(NGOs) [5,6]. Support for CBFM is based on the notion that people who
depend on marine resources are often the best informed about local
resource contexts, the most committed to sustainable harvesting, and
will thus develop more effective and appropriate management practices
to address local objectives [7,8].
Despite a substantial shift towards CBFM for small-scale fisheries
governance, particularly in the developing world, empirical evidence
suggests that the outcomes of CBFM for people and ecosystems are
mixed [9,10]. For example, community management benefited fishers
in Indonesia by contributing to poverty alleviation, but the benefits did
not endure after the project implementation period [11]. Alternatively,
evidence from inland Africa suggests that the transition to CBFM
redistributed power in a way that excluded local fishers from resource
decision-making processes [12]. Ultimately, effective and sustainable
fisheries governance requires more systematic understandings of the
attributes that render some management strategies more effective than
others [13,14].
Considerable efforts have been directed towards the design and
implementation of CBFM [15–17]. By comparison, the factors that
influence successful CBFM outcomes remain inadequately understood.
In part, this stems from the fact that few CBFM projects meet the data
requirements for formal impact evaluations such as before-after con-
trol-impact experiments [13,18]. The reasons for this are many. First,
many CBFM efforts are low intensity so as to protect the “bottom-up”
nature of the initiative, but also to ensure that CBFM is replicable in
http://dx.doi.org/10.1016/j.marpol.2017.05.008
Received 2 February 2017; Received in revised form 5 May 2017; Accepted 5 May 2017
⁎
Corresponding author at: Australian Research Council Centre of Excellence for Coral Reef Studies, James Cook University, Townsville, QLD 4811, Australia.
E-mail addresses: jessicalblythe@gmail.com, jessica.blythe@jcu.edu.au (J. Blythe).
Marine Policy 82 (2017) 50–58
0308-597X/ © 2017 Published by Elsevier Ltd.
MARK