RECOMMENDATIONS, ACKNOWLEDGEMENTS, REFERENCES

 

RECOMMENDATIONS

CBA is an economic activity that will almost certainly expand in the short term, and is very likely to continue into the long term for many species. CBA is practised because it has become necessary as a livelihood, as an alternative means to controlling access of fishery resources, to meet market demand and, if practised properly, to enhance yield.


It does not necessarily, or even desirably, lead to HBA and does not demonstrably take pressure off wild stocks. For example, despite decades of Anguilla CBA, successful HBA is far from certain. Moreover, new species will likely become the focus of CBA while a few species will eventually move to successful hatchery production. Even in the latter case, as for groupers, a mixed model might persist whereby both HBA and CBA practices occur; it took over 10 years to reach successful grouper HBA for just a few species while many others (e.g. the Hong Kong grouper Epinephelus akaara) continue to be exploited under CBA despite capacity for HBA. The bottom line, it seems, is that CBA is here to stay and means must be sought to ensure its sustainable practice. Whether or not CBA, or HBA, will take pressure off wild fisheries is entirely another matter that would require specific legislation whereby CBA development is balanced by a corresponding and specific reduction of fishing pressure in concert with CBA expansion.

 

While, for example, the supply of hatchery-reared juveniles for backyard grow-out of groupers in Indonesia is claimed to have reduced cyanide fishing by replacing fishing with culture practices, there are no quantitative data to support this and no relevant legislation to mandate a the shift from capture to culture.
CBA is truly a hybrid between capture fisheries and aquaculture, with many of the advantages and disadvantages inherent in both activities. Important as an alternative livelihood, CBA also offers opportunities for the development of HBA. However, CBA is not necessarily a stepping stone between the two but rather an activity in its own right which will certainly continue. Because of the impacts and implications of CBA, it needs to be acknowledged as distinct sector and integrated and managed accordingly as a specialized, albeit little understood type of fishery. This means that the objectives of CBA must be clear, the risks identified, activities clearly defined, and practices developed or modified to address the negative aspects of the practice and enhance the benefits.
Based on the present review, eight specific recommendations are proposed to improve CBA practices in a way that will address many of the shortcomings documented:
• Precautionary approach and FAO Code of Conduct: There is a need to adopt the precautionary approach in CBA. There is a little biological understanding of early life history stages of species under CBA, and they receive negligible management attention. Moreover, the principles and guidelines of the FAO Code of Conduct for Responsible Fisheries should be applied because CBA involves capture fisheries.
• Mortality: There is a need to be realistic. While very early settlement stage larvae almost certainly suffer high mortality reducible by judicious removal from the wild and culture, propagules are not infinite for any species and the highly focused removal of millions to billions of seed will ultimately compromise stocks. Much CBA is practised on older post-settlement stages, in effect capture fisheries of juveniles, that need to be managed accordingly. Management that takes such realities into account need to be developed for many of the CBA species reviewed, and training and outreach is needed to reduce mortalities associated with a range of capture, transfer and culture practices.
• Bycatch: In addition to a high capture and culture mortality, there is, for many of the representative species reviewed, a high and often diverse associated bycatch.
This aspect of these fisheries can severely undermine the perceived advantages of CBA and measures should be made to develop more selective gears, or, fish in a way that minimizes wasteful bycatch.
• Objectives of CBA: The objective(s) of CBA must be clear if it is to capitalize on its potential and be managed and practised sustainably. Nowadays, CBA is largely an economic activity involving many high value species and not necessarily practised with the objective of producing basic, low-cost, seafood for sustenance.
It is, therefore, not currently practised as an alternative to fishing for food per se. Rather, it is as an economic activity in its own right, provides livelihoods, and, perhaps, is a means of gaining access to, and control of, increasingly limited resources earlier in their life history. It is only by acknowledging its role in practice that it can be managed effectively.
• Management: Management and better practices are possible only when activities are recognized, acknowledged and documented. CBA needs to be monitored and a better understanding of its direct and indirect impacts on targeted and nontargeted (bycatch) species considerably better understood. Other impacts, such as the effects of fishing gears, have been widely acknowledged and need effective management. Considerations of equity of resource access and user conflicts should be factored into management plans. Moreover, even HBA will depend for genotype refreshment from natural broodstock, such that wild populations will continue to need management. Finally, for managing late stage CBA (e.g. as for tuna), if most juveniles removed are likely to survive to adulthood, it makes more biological sense to manage by number of fish in a quota, rather than by weight as is currently done.
• CBA to HBA: It is clear that not all CBA leads to HBA and that mixed models are likely to persist long into the future. For many species, the focus on CBA versus HBA will depend on economic factors and whether CBA moves to HBA is both an economic and a technical matter, and far from inevitable. It may not even be desirable that all mariculture becomes HBA because of the possible control on seed supply by big business that HBA would foster, with possible negative impacts on wild seed prices and livelihoods of seed collectors. Given the inevitable and probably advisable, mixed model, the relationships between the two activities need to be acknowledged and managed practically and realistically.
• Definitions: The perspectives on how to manage, understand and monitor CBA are heavily shaped by how it is defined and what are the objectives in its application.
The recent introduction of the term CBA has been enormously helpful in better understanding and more easily discussing it. However, the documentation of CBA-cultured species in FAO records appears to be unnecessarily complicated and somewhat misleading. We propose a simpler and more representative set of definitions that directly reflect the nature of CBA in relation to wild resources.
For documenting and reporting culture production, we suggest two major categories; “hatchery” and “non-hatchery” sources of seed. Under non-hatchery sources, a subdivision could be used to distinguish between “growing-out” (of eggs, larvae, very early post-settlement stages) and “fattening” (the increase in bulk of settled/juvenile animals or their maintenance until retail). The former would include spat, post-larvae and small juveniles of fish and invertebrates and the latter would include large juveniles and young adults, for example of groupers and tunas. The intention is to distinguish between seeds taken at very high natural mortality stages and seeds taken once natural mortality has likely dropped to near adult levels. Both categories of non-hatchery produced seed would need to be managed and monitored.
• Species cultured: The culture of fish centuries ago began with CBA practised on herbivorous and omnivorous species, such as carps, milkfish, mullets, eels and tilapias to address basic needs for food, while expensive, luxury, and carnivorous species appeared only after the 1940s (Ling, 1977; Beveridge and Little, 2002). If CBA is to be used for food security there has to be a greater focus on species that can provide cheap food and do not involve the many problems associated with carnivores in culture and capture. Again the “Objectives” of CBA need to be clear, i.e. why do we need CBA and how can we use it to best advantage? There are tradeoffs to different objectives and some are mutually exclusive: provision of livelihoods for seed supply may compromise the fishery of adults of the same stock; the use of ponds for expensive grouper culture may mean that cheaper food fishes are displaced; in both cases poorer communities might lose out; the removal of massive volumes of fish feed may compromise the feed species (many of them the young of cheap fish consumed by humans) captured, or the ecosystems they belong to. Without clear principles and guidelines, and a realistic evaluation of the constraints and problems associated with CBA, this form of culture cannot realize its full potential and, far worse, may further compromise natural marine resources and human communities.


ACKNOWLEDGEMENTS


The authors are most grateful to the following for their assistance in providing information and support that enabled the completion of this report: Mr Jinbiao Liu (retired Senior Fisheries Officer, Fujian Province Fisheries Administration, China), Dr Vu Ngoc Ut (College of Aquaculture and Fisheries, Can Tho University, Viet Nam), Mr Hanshen Wang (Fujian Province Fisheries Research Institute, China), Ms Maria Lourdes Cobo (Centro Nacional de Acuicultura e Investigaciones Marinas, Ecuador) and Ms Rachel Wong (Division of Ecology & Biodiversity, University of Hong Kong, China Hong Kong SAR). They are also grateful for funding from the Government of Japan (through a Trust Fund arrangement) for preparing the review paper, and from the Research Grants Council in China Hong Kong SAR for supporting Dr Min Liu and to the Swire Institute of Marine Science and the Department of Ecology & Biodiversity of the University of Hong Kong for general logistic support.


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