Efficiency of Artificial Reefs for Local Communities Over Time

Efficiency of Artificial Reefs for Local Communities Over Time

Jorge H. P. Ramos, Miguel Neves dos Santos
Copyright: © 2022 |Pages: 20
DOI: 10.4018/978-1-6684-2344-8.ch001
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Abstract

Half a century ago it was thought that artificial reefs (AR) would be the solution to numerous problems. After the disappearance of this panacea, people started to think about AR more from the point of view of their efficiency and usefulness. However, some issues persist. Will it be possible some time after the reef deployment to reach the goals initially outlined by the proponents? It is very important to get answers to this and other questions to know about the efficiency of reef deployment. However, answers to these questions are not always easy to obtain. The AR are submerged, often difficult to access, and the resources available for research are generally scarce and very well delimited in time. In this chapter, the authors approach the case study of artificial reefs deployed off the Algarve coast in the south of Portugal over time. The focus will be on the contribution of reef structures to human activities at economic and social levels, which in some ways have benefited from these improvements on the seabed.
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Introduction

From the point of view of efficiency, when designing an artificial reef (AR), several objectives to be achieved after the implementation of the structures must be anticipated (Seaman & Jensen, 2000; Ramm et al. 2021). To achieve efficiency in the project, it is equally important to consider from the beginning that a good development of the entire process will have to include the set of stakeholders interested and involved in the initiative, the monetary funds available, the geographic areas with potential for use and the selection criteria to be used (Claudet & Pelletier, 2004). The selection criteria cover several aspects such as: not only construction materials, size, or performance of the structures (Kim et al., 2021) and their typology (e.g., modules or ex-vessels), but also what purpose will the structures serve, what type of users will be covered, and which are the rules to follow to an adequate management of the areas where the structures were sunk (Bohnsack & Sutherland, 1985; Tunca et al., 2019). After all these initial assumptions have been considered, the modular construction or reuse of the structures is done, and the reef deployment is consummated (Martin, 2004).

Sometime after the reef deployment – that is, during the structure maturation process – it is convenient to verify to what extent the initially proposed objectives have been achieved. This long process makes it possible to determine whether the reef deployment has been efficient, either from a structural, ecological, social, or economic point of view, or another that has been defined (Seaman, 2000).

For example, as the deployment of reefs essentially consists in the creation of three-dimensional spaces that can mimic the habitats of certain organisms, what is initially done to verify the success of the deployment of reefs is to carry out scientific research on the progressive achievement of the colonization of living marine resources (Holland et al., 2021). It is of great importance to get answers to questions related to the types of living marine organisms that colonize the reefs in each geography and depth, or what type of ecological arrangements are formed on the different sides of the reef, regardless of if they are modules or another type of structures (Choi et al., 2002). This monitoring is essential, as if there is not an adequate colonization, this fact can be an indicator of a possible problem (Kolian et al., 2017). In such a case, reef efficiency is called into question.

After verifying reef colonization and evaluating its eventual biological and ecological success, it is important to understand how AR are accepted by potential human users (Adams et al., 2006). In turn, these potential users will empirically assess the usefulness of the structures relating them to the satisfaction achieved in their own activity, whether professional or recreational (Layman & Allgeier, 2020). The income derived from businesses that may eventually operate taking advantage of the reef's surplus value, enter in this process of assessing the efficiency of AR (Fletcher et al., 2011). For instance, it is possible to find the average wage that each worker in the primary sector earns (i.e., small-scale fisheries). The diversification of tourist activities of companies that promote sport fishing and leisure diving can also be evaluated. The efficiency of reef structures derives from the surplus that these firms will take from having more choice options to offer their clients (Monteiro, 2016).

The existence of high biodiversity in these reef structures is a fundamental factor to assess and consider the issue of ecological efficiency (Huddart, 2019). There may also be factors with a more negative predisposition that may influence a good performance in the efficiency of AR. These types of negative factors can often be related to siltation caused by undercurrents on some structures, or fishing gear that has been stranded or lost on some modules (Barber et al., 2009). In both cases there is a latent loss of reef efficiency. In these cases, it is essential to have an adequate identification of the problem and steps should be taken for a reef maintenance (Roseman et al., 2017).

Key Terms in this Chapter

Coastal Communities: Usually villages or small towns that employ many people that are highly reliant on coastal goods and services, namely sea resources and related activities. For example, fishers, scuba divers and tourism operators may benefit of coastal areas where there are diversified and abundant fish resources, as well as low pollution levels can be found.

Artificial Reef Supply: When there are artificial reef deployment structures promoted by decision entities. Depending on the type of structures and the objective of the project, artificial reefs supplied are generally available for different purposes including biodiversity promotion, coastal protection, fisheries enhancement.

Artificial Reef Stakeholders: All users or non-users that have interest in the structures either as primary, secondary, or external actors.

Algarve Coast: Is the southernmost region of Portugal mainland where most artificial reefs are deployed.

Artificial Reef Program: Between 1990 and 2003 occurred In the Algarve (south region of Portugal mainland), deployment actions promoted by the national fisheries and marine research institute (currently IPMA).

Artificial Reef Demand: When there are stakeholders (usually primary such as users) that seek artificial reefs as a complement or substitute for their professional (e.g., small-scale fishers) or recreational (e.g., scuba diving) activities.

Efficiency: The efficiency of artificial reefs can be seen from the point of view of the usefulness of the structures for the benefit of human activities (e.g., fishing, diving), so that there is no unnecessary waste of resources – materials, energy, money, time – and that the benefits achieved by the stakeholders be the desired ones.

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