ReviewLinking restoration ecology with coastal dune restoration
Introduction
For millennia, the coastal environment has been one of the preferred settings for urban, industrial and maritime development, and more recently, for mining, tourism and recreation (Nordstrom, 2008). Nearly 40% of the world human population lives within 60 km from the coast (Martínez et al., 2007), and it is expected that human encroachment on the coast will increase to 60% by 2020 (UNCED, 1992). Such a continuously growing population will result in an increasing human impact with the degradation or loss of coastal ecosystems. Of these, sandy beaches and coastal dunes are among the most damaged by human activities. Indeed, these unique ecosystems are increasingly becoming trapped between the expanding human populations and the effects of global climate change, such as sea level rise (Defeo and de Alava, 1995, Cencini, 1998, Nordstrom, 2000, Schlacher et al., 2007). These pressures act across multiple dimensions in time and space, and result in ecological impacts that occur at many temporal and spatial scales so that today the vast majority of beaches and coastal dunes are threatened by human activities (Nordstrom, 2008, Defeo et al., 2009).
Coastal dunes are degraded and lost because of a wide array of human actions and activities (Ketchum, 1972, Nordstrom, 2008), which can be aggregated into six groups: 1) housing and recreation; 2) industrial and commercial use; 3) waste disposal; 4) agriculture; 5) mining and 6) military activities. Typically, they alter coastal dynamics and natural processes, eliminate topographic variability, fragment, degrade or eliminate habitats, reduce biodiversity and threaten endemic species (Nordstrom, 2000, Nordstrom, 2008, Ayyad, 2003, Martínez et al., 2006, Martínez et al., 2013a, Martínez et al., 2013b, De Luca et al., 2011, Faggi and Dadon, 2011).
The increasingly rapid loss and degradation of coastal dunes clearly shows the urgent need to preserve these ecosystems, and, as much as possible, restore those that have been degraded. Different actions are already taking place to restore coastal dunes, and they span contrasting activities that range from revegetating and stabilizing the mobile substrate, in one extreme, to removing plant cover and increasing substrate mobility in the other (Martínez et al., 2013a, Martínez et al., 2013b). With such a wide array of restoration possibilities, it is necessary to evaluate the progress and success of restoration with clearly established criteria. To address this problem for coastal dunes (and any other ecosystem that is being restored), the Society for Ecological Restoration (SER, 2004) produced a list of attributes that are associated with ecosystem integrity, health and sustainability and that can be used to measure restoration success (Table 1).
The elements on this list (Table 1) cover different stages of ecosystem development and can be associated with the ecological theory of natural succession: “the natural recovery of ecosystems after the impact of disturbances” (Connell and Slatyer, 1977, del Moral et al., 2007). According to the ecological theory, restoration and ecological succession are similar in the sense that they share several elements: site colonization (natural or after human intervention); vegetation establishment (natural or assisted); structuring of ecosystem cycles, species assembly and biotic interactions. Finally, in the last successional stages (or after long-term restoration), the ecosystem is structurally complex and relatively resilient (Fig. 1).
The ecosystem (naturally recovering or restored) develops through similar processes that affect the ecosystem integrity, health (functionality) and resilience. In early successional stages (or early restoration actions), colonization occurs after natural dispersal, from seed banks or because of human intervention (plantations). These early colonizers ameliorate the environment and facilitate the colonization of late colonizers, which become established and modify the physical environment even further. After establishment, different species assemblages are integrated, biotic interactions intensify and soils develop (Fig. 1). The ecosystem develops gradually through these events.
Some of the more measurable attributes that are frequently used to monitor the progress of restoration and hence, ecosystem development and recovery, include (SER, 2004): a) community structure and composition (integrity); b) a handful set of ecological processes, such as nutrient cycling and species turnover during plant succession (health); and c) the ability to recover after the impact of additional disturbances by means of natural regeneration of the restored ecosystem (sustainability). The success of restoration based on these attributes has been monitored before, but not in the context of coastal dunes. For example, Ruiz-Jaen and Aide (2005) analyzed how restoration success was being measured in restoration projects that had been published in the peer-reviewed journal: “Restoration Ecology” from 1993 to 2003. In general, they found that different elements were used to measure restoration success, but they were not always related to the three ecosystem attributes. They only registered two studies on coastal dune restoration that referred to restoration actions after mining in South Africa (van Aarde et al., 1996, van Aarde et al., 1998).
Because of the relevance of restoring coastal dunes and assessing the success of these restoration actions, our goal was to review how the relative progress of ecological restoration actions has been assessed for coastal dunes, according to the ecosystem attributes outlined by SER: namely, integrity, health and sustainability and that are derived from the ecological theory of natural succession (Gann and Lamb, 2006). Recommendations on new paths that are needed to improve the activities for coastal dune restoration were derived from this analysis.
Section snippets
Methods
Peer reviewed articles published between 1988 and 2012 were included in the assessment. Articles were extracted from four digital databases (ISI Web of Science, EBSCO, SCOPUS, and JSTOR). Articles from two journals that publish papers in restoration ecology (Ecological Restoration and Journal of Coastal Conservation) but are not abstracted in the databases were included in the assessment. Articles were extracted by searching the terms ‘coastal dune’, ‘restoration’ and ‘revegetation’ within the
General trends
Since 1988, we found a total of 150 articles. From these, only 67 evaluated restoration efforts or monitored restoration cases in non-urbanized landscapes (wilderness approach) and assessed the progress of restoration. The rest only mentioned “restoration” but these studies did not exactly focus on restoration but considered that the studies “might be useful” for restoration activities. Thus, these studies were omitted from our analyses. In general, the number of published articles on coastal
Coastal dune restoration: different aims and different methods
Coastal dune ecosystems are dynamic and diverse, and the geomorphic and ecological characteristics vary around the world. The flora and fauna that inhabit the many habitats found here is equally diverse and dynamic, as well as the disturbance drivers affecting these ecosystems. In consequence, the restoration of coastal dunes is neither simple nor straightforward: it involves a wide array of activities, because no single “best” way exists to restore a dune. Many scenarios of recovery and many
Acknowledgments
This study was financed by grant FOMIX Veracruz-CONACYT (37009) and SEMARNAT-CONACYT (23669). DL sincerely thanks the Mexican Government and CONACYT for her PhD scholarship (CONACYT 275429/224619). Martínez, Gallego-Fernández and Hesp thank their respective institutions for support. We also thank Dr. Karl Nordstrom and Dr. Nancy Jackson and the anonymous reviewers for their thorough reviews of the manuscript. No dunes were harmed in the creation of this paper.
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2022, Landscape and Urban PlanningCitation Excerpt :The restoration of plant assemblages, by planting native species and removing invasive species, in coastal dunes can have significant biodiversity benefits by, for example, increasing bird species richness by increasing structural complexity through plantings and creating more suitable habitat (Munro et al. 2011). Restoring coastal dune plant assemblages is therefore an important biodiversity and ecosystem service intervention for coastal managers (Lithgow et al. 2013). Rarely, however, have quantitative planning steps been undertaken to identify and/or prioritise key areas and actions for coastal dune restoration (Gilby et al. 2018).
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Current address: Universidad Autónoma de Baja California, Ensenada, Mexico.