Elsevier

Marine Policy

Volume 133, November 2021, 104737
Marine Policy

Unravelling Lessonia trabeculata management in coastal areas of the Atacama region of northern Chile through a DPSIR approach: Insights for sustainable plans

https://doi.org/10.1016/j.marpol.2021.104737Get rights and content

Abstract

Subtidal Lessonia trabeculata is one of the primary kelp resources of northern Chile. It is an ecosystem engineer that provides habitat, shelter, and food for invertebrates and fish. This fishery has been developed by a collection of stranded algae carried out by legally registered fishers and illegal collectors in open-access areas and management and exploitation areas for benthic resources. Due to the current high demand on the international market, the collection of dead plants is supplemented by direct extraction. In response, a management plan has been implemented to regulate extraction efforts and institute annual quotas. The dynamics of the L. trabeculata fishery in the Atacama region over 20 years were evaluated using the conceptual framework of the driver-pressure-state-impact-response (DPSIR) approach. The fishing dynamics are strongly conditioned by price fluctuations, promoting the growth of fishing efforts (pressure) in response to economic indicators (driving forces). This often leads to a high volume of extractions of resources (impact) reflected in the increase in extractors and landings in spite of the establishment of quotas (responses), that generate intense pressure on local populations of algae and other commercially important fish and invertebrates (state). A lack of knowledge was detected regarding population aspects and its associated communities. Consequently, this kelp has been mismanaged without a specific focus on this species. Finally, the indicators included in the present DPSIR analysis enable a global understanding of the L. trabeculata fishery, and it should be considered as a basis for future studies and the implementation of resource management strategies.

Introduction

The brown macroalgae Lessonia trabeculata inhabits the rocky subtidal zone (up to 40 m deep) of the Pacific coast of South America, from the south of the Peruvian to Chilean coast [1]. This kelp is the most abundant brown macroalgae in subtidal environments throughout much of the Chilean coast (18–42°S) [2], [3]. L. trabeculata supports essential ecological assemblages, forming habitats [4], [5], [6], [7] and providing services and ecosystem functions, such as food sources and shelters for different species of invertebrates and fish [8], [9], [12] and a reduction of wave intensity and water flow [13], [14].

L. trabeculata is a resource of great economic importance for the artisanal fishing sector of the country, with landings that exceed 18,000 tonnes per year [15] and social contributions with a direct workforce of more than 4000 fishers in the last decade [16]. Its exploitation began in the 1980s with the collection of stranded L. trabeculata algae [2]. The most significant interest in Lessonia spp. resources coincided with the collapse of many benthic fisheries, prompting many fishers to become collectors and extractors of brown algae [3], [17]. In the last 20 years, the landing of this brown algae has shown a substantial historical maximum first in 2013 and later in 2017 due to the growing demand for alginates from the international market in countries such as China, Japan, Norway, and France [16]. Additionally, the abalone industry requires L. trabeculata for aquaculture feeding [18].

The contribution to kelp landings on the coast of the Atacama region is one the most important for Chilean production (2017–2018), constituting 32% of the total; the annual landing of L. trabeculata is approximately 25,000 tonnes. At the Atacama regional level, the fishery generates 97,748 USD and 4000 jobs for the artisanal fishing sector [16]. This fishery presents problems, such as the rapid filling of annual harvest quotas, contending with illegal extraction activities, and the use of indiscriminate extraction techniques [16]. These aspects hamper management plans and governance.

By 2005, the increase in resource value propelled the change from dead algae collection due to landing (natural mortality) to direct extraction [3], [18]. Direct harvesting by means of detaching algae from the rocky substrate using crowbars negatively affects the density, size, and morphology of algae, changing biological communities into predominantly barren ground [19], [20]. In this current scenario of a notable increase in the extractive pressure on kelp, the Undersecretary of Fisheries and Aquaculture (SUBPESCA) developed a programme to regulate fishing and research that has been implemented since 2005. The programme is based on the biological and fishing regulations that are part of management plans to guarantee the sustainability of kelp resources as measured by biological aspects: minimum extraction sizes, appropriate removal methods, extractive closures, and annual quotas [18]. Additionally, extra measures have been suggested, such as area rotation; the intercropping of plants; the repopulation, restoration, or creation of new management areas [3], [21], [22], [23], [24], [25]; and the establishment of marine reserves to foster kelp protection. All of these specific management strategies aim to regulate landing and promote sustainable exploitation.

The commercial exploitation of L. trabeculata is closely linked to the fisheries activity of the Lessonia nigrescens complex. They share aspects such as extraction agents and the methods of extraction and mincing. However, the same amount of information about the population and community aspects of L. trabeculata are not available, which requires specific management measures [26]. The sustainable development for wild L. trabeculata fisheries requires an understanding of the population dynamics and the ecosystems that they support. Therefore, it is necessary to design and develop a conceptual framework for a sustainable management programme that incorporates the dynamic complexity of the dimensions of the ecological-economic-social system related to this type of fishery [27], [28].

In this context, an analysis based on an integrated management framework [30], [31] is required to identify and unravel the different factors that govern the sustainability of the fisheries of L. trabeculata. The purpose is to evaluate the economic, social, and ecological conflicts in its fishery derived from the implementation of a single general brown algae management programme in northern Chile. One of the tools available and developed by the OECD (Organisation for Economic Cooperation and Development, 1993) and EEA (European Environment Agency, 1995) is the driver-pressure-state-impact-response (DPSIR) conceptual framework. DPSIR is a simple tool for contextualising major environmental issues, contributing to the decision-making process and regulatory enforcement. It also facilitates the inclusion of modules linked to anthropic activities, appropriately distributing the systems analysed, and selecting the relevant indicators for their functioning [42]. This conceptual framework is particularly relevant for assessing the status of the L. trabeculata alga fishery in northern Chile. In order to better understand the past and current problems related to fishery sustainability (e.g., overexploitation and price speculation) [32], [33], [34], [35], [36], [37], it allows us to identify cause-effect relationships among the selected indicators in drivers, pressures, state, impact and response [29] and facilitates communication channels among users, scientists, and decision-makers, among others [33].

This study evaluated the management of an L. trabeculata fishery by using the DPSIR conceptual framework. The main goals were to (i) identify and classify the principal indicators (socioeconomic, ecological, and administrative) affecting the performance of this fishery; (ii) chronologically review the management measures (legal, management, and operational) established for fishing regulations; and (iii) propose considerations for future management plans based on current gaps identified by DPSIR analysis.

Section snippets

Study area and fishery characterisation

The Humboldt Current System, one of the most productive ecological systems in the world, is characterised by the elevation of nutrient-rich subsurface waters and a low oxygen content [38], [39]. It has a significant influence on the coastal edge of Atacama (26–29°S); throughout the Atacama region, L. trabeculata kelp is found in this subtidal environment within numerous patches in bays and inlets [17]. The extraction of this resource is carried out by artisanal fishers and divers registered

Drivers

Concerning the economic dimension, the variations in the average annual ‘kelp beach price’ (first sale value) between 2000 and 2018 showed low prices in the early years (38 USD per tonne), but then prices rose, and the first maximum was reached in 2010, with a cost of 425 USD per tonne. A second maximum peak was reached in 2015, with a value of 359 USD per tonne (Fig. 3a, Table 1). This progressive rise in beach prices was a consequence of sustained growth in international market demand.

Kelp fisheries under a high international demand scenario

In recent years, due to the growing demand on the international markets [49], there has been an evident increase in the first sale value (driving forces) [15] and, consequently, high pressure on this resource (pressure), which does not imply good profits for fishers, since many of them have lower profit percentages than those of the intermediary seller [82]. This scenario is amplified in periods when the other kelp, L. nigrescens, has decreased in price (driving forces). As a result, many

Conclusions

DPSIR analysis applied to the L. trabeculata kelp management plan (in the Atacama Region) was revealed to be useful for the identification and organisation of causal relationships between different components based on current knowledge and conflicts presented in the brown algae resource management plans in northern Chile.

In recent years, there has been growing interest in the exploitation of L. trabeculata due to its high commercial value when the prices of L. nigrescens decrease. Since 2013,

CRediT authorship contribution statement

All authors certify that they have participated sufficiently in the work, including participation in the concept, design, analysis, drafting, or revision of the manuscript.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgments

This work was conducted as part of the Postdoctoral Fellowship Universidad de Atacama 2018–2020 Decreto Exento RA N° 366/506/2019 of the first and second author funded by the Vicerrectoría de Investigación y Postgrado de la Universidad de Atacama (VRIP), Chile. The authors thank to the director of SERNAPESCA Atacama Guillermo Mery for the information provided, to A. Diu for the artistic contribution. E. Bonnail thanks to ANID/FONDECYT (11180015).

References (98)

  • S. Knudsen et al.

    Identifying drivers for fishing pressure. A multidisciplinary study of trawl and sea snail fisheries in Samsun, Black Sea coast of Turkey

    Ocean Coast. Manag.

    (2010)
  • J.H. Martins et al.

    A review of the application of driving forces – Pressure – State – Impact – Response framework to fisheries management

    Ocean Coast. Manag.

    (2012)
  • J.P. Atkins et al.

    Management of the marine environment: integrating ecosystem services and societal benefits with the DPSIR framework in a systems approach

    Mar. Pollut. Bull.

    (2011)
  • A. Gregory et al.

    A problem structuring method for ecosystem-based management: the DPSIR modelling process

    Eur. J. Oper. Res.

    (2013)
  • C. Ojeda-Martínez et al.

    A conceptual framework for the integral management of marine protected áreas

    Ocean Coast. Manag.

    (2009)
  • J.H. Martins et al.

    A review of the application of driving forces – Pressure – State – Impact – Response framework to fisheries management

    Ocean Coast. Manag.

    (2012)
  • M.N. Miranda et al.

    Microplastics in the environment: a DPSIR analysis with focus on the responses

    Sci. Total Environ.

    (2020)
  • F. Tala et al.

    Growth and loss of distal tissue in blades of Lessonia nigrescens and Lessonia trabeculata (Laminariales)

    Aquat. Bot.

    (2005)
  • M. Ortiz et al.

    Network properties and keystoneness assessment in different intertidal communities dominated by two ecosystem engineer species (SE Pacific coast): a comparative analysis

    Ecol. Model.

    (2013)
  • W. Stotz et al.

    Vertical distribution of rocky subtidal assemblages along the exposed coast of north-central Chile

    J. Sea Res.

    (2016)
  • R. Hilborn

    Defining success in fisheries and conflicts in objectives

    Mar. Policy

    (2007)
  • M. Ortiz

    Pre-image population indices for anchovy and sardine species in the Humboldt Current System off Peru and Chile: years decaying productivity

    Ecol. Indic.

    (2020)
  • S.W. Purcell et al.

    Distribution of economic returns in small-scale fisheries for international markets: a value-chain analysis

    Mar. Policy

    (2017)
  • L. Campos et al.

    Evaluating the macroscopic system properties of kelp species planted on two artificial reefs: implications for the restoration of perturbed subtidal areas

    Estuar. Coast. Shelf Sci.

    (2021)
  • B. Hermosillo-Nuñez et al.

    Keystone species complexes in kelp forest ecosystems along the northern Chilean coast (SE Pacific): improving multispecies management strategies

    Ecol. Indic.

    (2018)
  • S. Jørgensen et al.

    Ecosystems emerging growth

    Ecol. Model.

    (2000)
  • M. Ortiz

    Mass balanced and dynamic simulations of trophic models of kelp ecosystems near the Mejillones Peninsula of northern Chile (SE Pacific): comparative network structure and assessment of harvest strategies

    Ecol. Model.

    (2008)
  • M. Ortiz

    Robustness of macroscopic-systemic network indices after disturbances on diet-community matrices

    Ecol. Indic.

    (2018)
  • M. Ortiz et al.

    Macroscopic network properties and short-term dynamic simulations in coastal ecological systems at Fildes Bay (King George Island, Antarctica)

    Ecol. Complex.

    (2016)
  • J.V. Vásquez et al.

    Diversidad, abundancia y variabilidad temporal de ensambles de macroalgas del submareal rocoso del norte de Chile

  • J.A. Vásquez

    Production, use and fate of Chilean Brown seaweeds: resources for a sustainable fishery

    J. Appl. Phycol.

    (2008)
  • M. Villegas et al.

    Macrocystis integrifolia and Lessonia trabeculata (Laminariales; Phaeophyceae) kelp habitat structures and associated macrobenthic community off northern Chile

    Helgol. Mar. Res.

    (2007)
  • A. Pérez-Matus et al.

    Exploring the effects of fishing pressure and upwelling intensity over subtidal kelp forest communities in central Chile

    Ecosphere

    (2017)
  • M. Villegas et al.

    Effect of foresting barren ground with Macrocystis pyrifera (Linnaeus) C. Agardh on the occurrence of coastal fishes off northern Chile

    J. Appl. Phycol.

    (2019)
  • N. Riquelme-Pérez, C.A. Musrri, W.B. Stotz, O. Cerda, O. Pino-Olivares, M. Thiel, Coastal fish assemblages and...
  • R. Steneck et al.

    Kelp forest ecosystems: biodiversity, stability, resilience and future

    Environ. Conserv.

    (2002)
  • M. Graham

    Effects of local deforestation on the diversity and structure of southern California giant kelp forest food webs

    Ecosystems

    (2004)
  • J. Geist et al.

    Habitat recovery and restoration in aquatic ecosystems: currentprogress and future challenges

    Aquat. Conserv. Mar. Freshw. Ecosyst.

    (2016)
  • J. Rosman et al.

    A field investigation into the effects of a kelp forest (Macrocystis pyrifera) on coastal hydrodynamics and transport

    J. Geophys. Res.

    (2007)
  • C. Layton et al.

    Resilience and stability of kelp forests: the importance of patch dynamics and environment engineer feedbacks

    PLoS One

    (2019)
  • Servicio Nacional de Pesca y Acuicultura (SERNAPESCA), 2018....
  • Subsecretaria de Pesca y Acuicultura (SUBPESCA), 2020. 〈http://www.subpesca.cl/portal/616/w3-article-85023.html#/〉....
  • J. González, C. Tapia, A. Wilson, J. Garrido, M. Ávila, Estrategias de explotación Sustentable Algas Pardas en la Zona...
  • J.A. Vásquez et al.

    The Lessonia nigrescens fishery in northern Chile: “how you harvest is more important than how much you harvest”

    J. Appl. Phycol.

    (2012)
  • J.A. Vásquez et al.

    Ecological effects of harvesting Lessonia (Laminariales, Phaeophyta) in central Chile

    Hydrobiologia

    (1990)
  • J.A. Vásquez

    Ecological effects of brown seaweed harvesting

    Bot. Mar.

    (1995)
  • J.A. Vásquez et al.

    Repopulation of intertidal areas with Lessonia nigrescens in northern Chile

    J. Appl. Phycol.

    (1995)
  • A.J.M. Vega et al.

    Monitoring the sustainability of Lessonia nigrescens (Laminariales, Phaeophyceae) in northern Chile under strong harvest pressure

    J. Appl. Phycol.

    (2014)
  • R. Westermeier et al.

    Holdfast fragmentation of Macrocystis pyrifera (integrifolia morph) and Lessonia berteroana in Atacama (Chile): a novel approach for kelp bed restoration

    J. Appl. Phycol.

    (2016)
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