Research Ideas and Outcomes :
Methods
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Corresponding author: Dimitra Petza (d.petza@marine.aegean.gr)
Academic editor: Editorial Secretary
Received: 22 Jun 2021 | Accepted: 07 Sep 2021 | Published: 26 Oct 2021
© 2021 Dimitra Petza, Panagiotis Anastopoulos, Marta Coll, Serge Garcia, Michel Kaiser, Stefanos Kalogirou, Irene Lourdi, Jake Rice, Marija Sciberras, Stelios Katsanevakis
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Petza D, Anastopoulos P, Coll M, Garcia SM, Kaiser M, Kalogirou S, Lourdi I, Rice J, Sciberras M, Katsanevakis S (2021) The contribution of Area-Based Fisheries Management Measures to Fisheries Sustainability and Marine Conservation: a global scoping review protocol. Research Ideas and Outcomes 7: e70486. https://doi.org/10.3897/rio.7.e70486
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Objective: This scoping review (ScR) aims to identify and map the evidence base on the contribution of area-based fisheries management measures (ABFMs) to fisheries sustainability and marine conservation. Emphasis will be given to the research that has been conducted in terms of the methodologies applied and the key findings acknowledged.
Introduction: ABFMs have been used for centuries and are present in modern fisheries management plans and regulations. Although ABFMs are commonly related to the sustainable exploitation of the target species of the managed fishery, they may also be considered as wider conservation measures, in the cases where their outcomes include the protection or reduction of impact on biodiversity or ecosystem structures and functions.
Inclusion criteria: Studies that perform an assessment of the contribution of ABFMs on either fisheries sustainability or on area-based marine conservation (or both) will be considered. All types of ABFMs in the marine realm globally, which are established as management measures by any type of designation authority or jurisdiction and for any type of fishing activity, gear, target species and/or habitats will be considered. Peer-reviewed and grey literature will be included. There will be no search limitations applied by year of publication. Studies in English, French, Greek, Italian, Spanish and Swedish will be reviewed.
Methods: The ScR will be conducted in accordance with the JBI (Joanna Briggs Institute) methodology. The PRISMA (Preferred Reporting Items for Systematic Reviews and Meta-Analyses) extension for ScRs will guide the protocol. The bibliographic databases to be searched include Scopus and Web of Science. Sources of grey literature will include databases, pre-print archives, organisational websites and web-based search engines. The design of the search strategy will be guided by a librarian/ information specialist. The Zotero software, Sysrev platform and EviAtlas tool will be used for data management, extraction and presentation. Data will be extracted by two reviewers. Tables, graphs and maps along with a narrative summary of the outcomes will be presented.
area-based marine conservation; fisheries closures; fisheries restricted areas; fisheries spatial measures; fisheries spatiotemporal measures
Area-based fisheries management measures (ABFMs) i.e. permanent or temporal restrictions on fishing activities applied at specific geographic areas, are formally established, spatially defined fishery management measures, implemented to achieve one or more intended fishery outcomes. The outcomes of these measures are commonly related to sustainable use of resources by the fishery (
Although ABFMs are commonly related to the sustainable exploitation of the target species of the managed fishery, they are increasingly being considered as wider conservation measures, in the cases where their outcomes include the protection or reduction of impact on biodiversity components, non-commercial species at risk, habitats or ecosystem structures and functions (
ABFMs’ performance may be assessed in relation to their contribution to fisheries’ sustainability as well as to broader conservation. Assessing the contribution of ABFMs to fisheries sustainability, commonly the primary objective of a conventional ABFM, is of vital importance to evaluate its effectiveness and readjust the measures applied to obtain optimal performance in the context of the explicit management objective(s). According to article 7.6.8 of the FAO Code of Conduct for Responsible Fisheries, “The efficacy of management measures and their possible interactions should be kept under continuous review. Such measures should, as appropriate, be revised or abolished in the light of new information” (
Besides contributing to fisheries sustainability, the contribution of ABFMs to marine conservation is also of great significance, especially within the OECMs concept. As is evident by the term and also by Criterion C of the CBD Decision 14/8 (
A preliminary search of Scopus and Web of Science was conducted and no current or underway systematic reviews focusing on both the fisheries sustainability and the marine conservation aspect of ABFMs, applied as purely fisheries management measures, were identified.
A synthesis, simultaneously considering the fisheries sustainability and the marine conservation aspect of ABFMs, would be of high relevance and interest for both the fields of fisheries and environmental management and policy. Consequently, it was deemed essential to perform a scoping review (ScR), as a starting point for such an evidence-based synthesis path. ScRs can be conducted to meet various objectives, such as to map the key concepts underpinning a research area, as well as to clarify working definitions and/or the conceptual boundaries of a topic (
The intent of this ScR is to provide insights into the evidence-based knowledge about ABFMs available to fisheries managers and policy-makers and also to provide information for the policy discussion of where an ABFM should be positioned along the continua of “effectiveness” in order to qualify as an OECM and contribute along with the MPAs to the attainment of the spatial targets set by CBD (
The overall research question that will guide this ScR is: What is the current knowledge about the extent to which ABFMs as fisheries management measures contribute to fisheries sustainability and marine conservation at a global scale? More specifically, the ScR will attempt to answer the following sub-questions:
The inclusion criteria of the protocol, which provide the basis on which sources will be considered for inclusion by the ScR, were developed in correspondence with the "Participants, Concept and Context, PCC" mnemonic and are detailed below.
This review will consider all types of ABFMs which were established as purely fisheries management measures by national, regional or international fisheries management authorities or organisations to support fisheries sustainability or broader ecosystem reasons for any type of fishing activity, gear, target species and/or habitats. Given the large range of ABFMs due to their different potential purposes and contextual parameters, examples of ABFM types that will be considered by the current review may include, amongst others, no fishing areas, fisheries restricted areas, spatio/temporal closures to fishing activities, total gear bans, marine areas for responsible fisheries etc. (see Table
Main types of Area-Based Fishery Management Measures (ABFMs) and their constraints in space, time and fishing activities as proposed by
TYPES OF ABFMS |
DESCRIPTION |
DIMENSION CONSTRAINED |
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Time |
Space |
Fishing Activities |
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Total closures for fisheries management reasons |
Measures usually adopted only when key target species are badly depleted or collapsed and other measures have not succeeded in limiting catches and rebuilding biomass and, hence, the total range of the fishery is closed. Depending on circumstances, the area might be closed sine die (permanent) or until the conditions that led to the closure disappear (temporary). |
PERM TEMP |
HS, EEZ, FG |
TC, PC |
No-fishing areas |
“No-fishing” areas can be instituted (a) in a zoning process of fishing and other economic activities in an EEZ, for different reasons. All fishing may be prohibited in areas so highly contaminated that eating seafood from them poses significant health risks or (b) where there are operational security concerns due to other human activities in the same area. |
PERM |
HS, EEZ, FG |
TC, PC |
Fishing zones |
Measures to allocate the available space and the resources therein, exclusively to types of fishing or fleets or to socio-economic groups, excluding others with the purpose to improve equity, allocate de facto some resources to some target groups of fishers, avoid conflict between fisheries using incompatible gears and reduce the risk of dangerous collisions. |
PERM |
EEZ |
PC |
Vulnerable Marine Ecosystems (VMEs) |
Closures of areas for the management of bottom-contracting gears because of the risks incurred by Vulnerable Marine Ecosystems (VMEs). |
PERM |
HS, PART |
TC, PC |
Benthic Protected Areas (BPAs) |
Voluntary closure to fishing activities for the vessels of the Southern Indian Ocean Deepwater Fishers Association (SIODFA) in deep-sea benthic habitats representative of a wide zone across the South Indian Ocean for the conservation of globally significant biodiversity, such as deep-water corals and sponges as well as sharks, tuna, marine mammals and commercially-important deep-sea fish species. |
PERM |
HS, PART |
TC, PC |
Ring Fencing |
Ring-fencing encloses a fishery in a delimited boundary beyond which it will not expand, limiting and containing the impact on biodiversity outside the boundary (within which other conventional ABFMs might also apply). It delimits implicitly or explicitly the extent of the areas historically and currently exploited by (certain) fisheries and intends to limit further development in all areas beyond that limit. Instead of protecting an area inside the fishing ground, it intends to limit expansion outside it. Established first by the sub-sector itself, it was later endorsed by the State. |
PERM |
EEZ, FG |
PC |
Fishery Restricted Areas (FRAs) |
Multipurpose spatial management tools to protect any kind of marine resource and habitat (e.g. aggregations of vulnerable sponges, seamount areas, coral reef building formations, seagrass meadows, spawning grounds and reproduction sites for fish resources etc.) from relevant fishing activities, in EEZs or the High Sea. |
PERM |
HS |
PC |
Rotational closures |
They involve temporary inter-annual and usually recurrent closures and re-opening of a set of areas (in sequence) to specific fisheries or gears. In the long-term, all areas in the sequence are fished on some pre-established multi-year schedule. They are often used, for example in some fisheries for sedentary benthic species, when efficient harvesting can rapidly take most of the stock in a local area and renewal of the stock takes several years. |
TEMP |
EEZ, PART |
PC |
Seasonal gear-specific closure |
Closed areas to a specific fishery or fishing gear for a period of time. The area and the time are usually the same every year, based on average time-space distribution of the element to be protected. They may be established to either prevent fishing on a target stock during a specific period of its annual life history cycle or prevent fishing during a period when a dependent or associated species, vulnerable to disturbance by the fishery, is especially exposed to fishing pressure. |
SEAS |
HS, EEZ, FG, PART |
PC |
Real-time spatial management (RTSM) |
A dynamic type of fishery management where the distribution of fishing effort and catches in space and time is obtained influencing fishers’ behaviour through economic incentives, increasing their collaboration, information sharing and innovation. High-density spatial information on resources and vessels, vessels monitoring systems and/or onboard observers and complex fishery models are needed. Third Party companies may be involved in collecting rapidly, processing and re-distributing the information which allows fishers to adjust their fishing to avoid bycatch species. Fishers’ fishing opportunities are then adjusted up or down depending on their performance in avoiding bycatch. |
RT |
PART |
PC |
Move on rules for fishing (real-time exclusion) |
They require set by set monitoring of a fishery, with a specific trigger for action specified in advance. If the monitoring finds the catch of a specific set exceeds the trigger, the fishing in that immediate area stops and the vessel must move a specified distance before trying another fishing event. This continues until the monitoring shows that the trigger is no longer exceeded. The area is immediately signalled to the management authority and fishing is excluded in the area for all vessels. The exclusion may be temporary or permanent. |
RT |
HS, EEZ, FG, PART |
PC |
Real-time incentives |
Economic instruments by which fishers are not formally excluded from operating in specific areas, but they pay for access to the areas they aim at, proportionally to the risk they create for the target or non-target resources. The payment is made with “impact credits” allocated to them which they can spend as they wish, selecting the areas in which they want to fish, balancing costs (in credits) and benefits. Fishing opportunities for the vessel are terminated when its credits are exhausted. The expected result is that a complex grid of small areas, precisely located (but not a priori closed and needing enforcement) remain lowly fished or unfished, offering protection to vulnerable ecological elements, without need for costly top-down prohibitions. |
RT |
PART |
PC |
Marine Managed Areas (MMAs) and Locally-Managed Marine Areas (LMMAs) |
MMAs are marine, estuarine and adjacent terrestrial areas, designated using federal, state, territorial, tribal or local laws or regulations intended to protect, conserve or otherwise manage a variety of resources and uses. They differ significantly from MPAs in that MMAs may not be permanent, but "must provide the same protection, for any duration within a year, at the same location on the same dates each year, for at least two consecutive years, even though they are expected to have continuity and the potential for permanence. LMMAs are areas of nearshore waters and coastal resources that are largely or wholly managed at a local level by the coastal communities, land-owning groups, partner organisations and/or collaborative government representative who reside or are based in the immediate area. Some areas may be closed or opened as needed within the LMMA. |
TEMP |
PART |
PC |
Marine areas for responsible fishing (MARF) |
Areas with important biological and sociocultural characteristics, delimited by geographical coordinates and any other mechanisms identifying their limits, within which fisheries are regulated to ensure particularly the use of fishery resources in the long term and for the conservation, use and management for which the Costa-Rica Institute of Fisheries and Agriculture (INCOPESCA) can count on the support of coastal communities and/or other Institutions. |
- |
- |
- |
Refugia |
Delimited areas established with the primary objective to conserve and contribute, naturally or artificially, to the development of fisheries resources, their reproduction, growth or recruitment and to preserve and protect the surrounding environment. |
- |
- |
- |
Territorial Use Rights in Fisheries (TURFs) |
A TURF intends to remove the condition of common property of the resources in a territory, allocating use and management rights explicitly to its owner, which can be an individual, a private enterprise, a cooperative, association or community. |
PERM |
PART |
PC |
Fishery community-based MPAs |
Clearly identified marine area, which is managed through law or other effective means while giving consideration to the utilisation form, with the aim of conserving the biodiversity that supports the healthy structure and function of marine ecosystems and/or ensuring sustainable use of ecosystem services. |
- |
- |
- |
The concepts that will be studied in this ScR are fisheries sustainability and conservation of marine biodiversity and how the contribution of ABFMs to these two concepts has been addressed so far in the scientific literature. All studies that perform an assessment of the contribution of ABFMs on either fisheries sustainability and/or on marine conservation will be considered. All types of methodologies applied, metrics used (e.g. ecological, economic or social) and key findings recorded on the effectiveness of ABFMs for fisheries sustainability and/ or marine conservation will be reviewed.
Studies on ABFMs in marine realm worldwide will be considered by the ScR established in territorial, international waters or exclusive economic zones and in all depths. Studies on ABFMs in inland or transitional waters will not be considered.
This ScR will consider peer-review literature (e.g. articles, reviews, book chapters, letters, editorials, books, data papers) retrieved by peer-reviewed literature databases and grey literature (e.g. non-published academic research, theses, policy papers, organisational papers and reports, conference abstract and papers) retrieved by pre-print archives, organisational websites and web-based search engines. Both experimental and observational studies will be reviewed. There will be no search limitations applied by year of publication, publication stage (final or in press), subject area and source type. All types of documents will be considered, except for evidence synthesis (e.g. systematic reviews, scoping reviews, rapid reviews etc.) or literature reviews. Language limitations will be applied in the literature search process to meet authors’ language competence. Thus, studies published in languages other than English, French, German, Greek, Italian, Spanish and Swedish will be excluded from the ScR.
The proposed ScR will be conducted in accordance with the
The Preferred Reporting for Systematic Reviews and Meta-Analyses extension for scoping reviews, PRISMA-ScR (
Preferred Reporting Items for Systematic reviews and Meta-Analyses extension for Scoping Reviews (PRISMA-ScR) Checklist. JBI = Joanna Briggs Institute; PRISMA-ScR = Preferred Reporting Items for Systematic reviews and Meta-Analyses extension for Scoping Reviews. * Where sources of evidence are compiled from, such as bibliographic databases, social media platforms and Web sites. † A more inclusive/heterogeneous term used to account for the different types of evidence or data sources (e.g. quantitative and/or qualitative research, expert opinion and policy documents) that may be eligible in a scoping review as opposed to only studies. This is not to be confused with information sources. ‡ The frameworks by
SECTION |
ITEM |
PRISMA-ScR CHECKLIST ITEM |
REPORTED ON PAGE # |
TITLE |
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Title |
1 |
Identify the report as a scoping review. |
1 |
ABSTRACT |
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Structured summary |
2 |
Provide a structured summary that includes (as applicable): background, objectives, eligibility criteria, sources of evidence, charting methods, results and conclusions that relate to the review questions and objectives. |
1 |
INTRODUCTION |
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Rationale |
3 |
Describe the rationale for the review in the context of what is already known. Explain why the review questions/objectives lend themselves to a scoping review approach. |
2 |
Objectives |
4 |
Provide an explicit statement of the questions and objectives being addressed with reference to their key elements (e.g. population or participants, concepts and context) or other relevant key elements used to conceptualise the review questions and/or objectives. |
4 |
METHODS |
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Protocol and registration |
5 |
Indicate whether a review protocol exists; state if and where it can be accessed (e.g. a Web address); and if available, provide registration information, including the registration number. |
N/A this is a protocol |
Eligibility criteria |
6 |
Specify characteristics of the sources of evidence used as eligibility criteria (e.g. years considered, language and publication status) and provide a rationale. |
5 |
Information sources* |
7 |
Describe all information sources in the search (e.g. databases with dates of coverage and contact with authors to identify additional sources), as well as the date the most recent search was executed. |
6 |
Search |
8 |
Present the full electronic search strategy for at least one database, including any limits used, such that it could be repeated. |
7 |
Selection of sources of evidence† |
9 |
State the process for selecting sources of evidence (i.e. screening and eligibility) included in the scoping review. |
7 |
Data charting process‡ |
10 |
Describe the methods of charting data from the included sources of evidence (e.g. calibrated forms or forms that have been tested by the team before their use and whether data charting was done independently or in duplicate) and any processes for obtaining and confirming data from investigators. |
8 |
Data items |
11 |
List and define all variables for which data were sought and any assumptions and simplifications made. |
8 |
Critical appraisal of individual sources of evidence§ |
12 |
If done, provide a rationale for conducting a critical appraisal of included sources of evidence; describe the methods used and how this information was used in any data synthesis (if appropriate). |
N/A this is a protocol |
Synthesis of results |
13 |
Describe the methods of handling and summarising the data that were charted. |
N/A this is a protocol |
RESULTS |
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Selection of sources of evidence |
14 |
Give numbers of sources of evidence screened, assessed for eligibility and included in the review, with reasons for exclusions at each stage, ideally using a flow diagram. |
N/A this is a protocol |
Characteristics of sources of evidence |
15 |
For each source of evidence, present characteristics for which data were charted and provide the citations. |
N/A this is a protocol |
Critical appraisal within sources of evidence |
16 |
If done, present data on critical appraisal of included sources of evidence (see item 12). |
N/A this is a protocol |
Results of individual sources of evidence |
17 |
For each included source of evidence, present the relevant data that were charted that relate to the review questions and objectives. |
N/A this is a protocol |
Synthesis of results |
18 |
Summarise and/or present the charting results as they relate to the review questions and objectives. |
N/A this is a protocol |
DISCUSSION |
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Summary of evidence |
19 |
Summarise the main results (including an overview of concepts, themes and types of evidence available), link to the review questions and objectives and consider the relevance to key groups. |
N/A this is a protocol |
Limitations |
20 |
Discuss the limitations of the scoping review process. |
N/A this is a protocol |
Conclusions |
21 |
Provide a general interpretation of the results with respect to the review questions and objectives, as well as potential implications and/or next steps. |
N/A this is a protocol |
FUNDING |
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Funding |
22 |
Describe sources of funding for the included sources of evidence, as well as sources of funding for the scoping review. Describe the role of the funders of the scoping review. |
9 |
The search strategy will aim to locate both peer-reviewed and grey literature. An initial limited search in Scopus was undertaken to identify relevant articles. The text words, contained in the titles and abstracts of relevant articles and the index terms used to describe the articles, were used to develop a full search strategy for Scopus and Web of Science Platform – Core Collection (see Suppl. material
For peer-review literature, the bibliographic databases to be searched include Scopus and Web of Science (Core Collection). Sources of grey literature to be searched will include grey literature databases (e.g. OpenGrey), pre-print archives (e.g. ArchivX), organisational websites (e.g. IUCN, FAO, ICES, NAFO, NEAFC, GFCM, WWF, Oceana, Greenpeace etc) and web-based search engines (e.g. Google). In web-based search, the first 500 hits will be screened. The design, development and execution of the search strategy will be guided by a librarian/ information specialist.
Following the search, all identified citations will be collated, uploaded to Zotero open-source reference management software (
Inclusion and exclusion criteria for the Scoping Review in correspondance with the "Participants, Concept and Context, PCC" mnemonic and evidence types and sources.
Inclusion criteria |
Exclusion criteria |
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PARTICIPANTS |
Area-based fisheries management measures (ABFMs) |
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CONCEPT |
Contribution of ABFMs to fisheries sustainability and marine conservation |
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CONTEXT |
Global marine realm |
Studies in:
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Studies in:
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EVIDENCE TYPES & SOURCES |
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Data will be extracted from papers included in the ScR by the two independent reviewers using a data extraction tool, i.e. a charting table aligned to the objective and the questions of the ScR (Suppl. material
The initial data extraction tool will be modified and revised when deemed necessary during the process of extracting data from each included evidence source. Modifications will be detailed in the final reporting of the ScR. If necessary, corresponding authors of papers will be contacted to request missing or additional data, where required.
The evidence synthesised by the ScR will be presented in correspondence to the review objective and questions. The data will be presented in both graphical and tabular form. The inclusion of the default graphical and tabular outputs provided by Sysrev (
This work is part of the first author’s PhD Thesis, conducted at the Department of Marine Sciences of the University of the Aegean. Any opinions, findings and conclusions or recommendations expressed in this material are those of the authors and do not necessarily reflect those of the authors’ affiliated institutions.
No specific grant was received from any funding agency in the public, commercial or not-for-profit sectors for this research.
The authors declare that there is no conflict of interest.
The entire search strategy (query string) applied in Scopus at 11 June 2021 and search results (number of articles retrieved).
A charting table aligned to the objective and the questions of the ScR, including specific details about the participants, concept, context, study methods and key findings relevant to the review objective.