Physical basis of coastal adaptation on tropical small islands
Small tropical islands are widely recognized as having high exposure and vulnerability to climate change and other natural hazards. Ocean warming and acidification, changing storm patterns and intensity, and accelerated sea-level rise pose challenges that compound the intrinsic vulnerability of small, remote, island communities. Sustainable development requires robust guidance on the risks associated with natural hazards and climate change, including the potential for island coasts and reefs to keep pace with rising sea levels. Here we review these issues with special attention to their implications for climate-change vulnerability, adaptation, and disaster risk reduction in various island settings. We present new projections for 2010–2100 local sea-level rise (SLR) at 18 island sites, incorporating crustal motion and gravitational fingerprinting, for a range of Intergovernmental Panel on Climate Change global projections and a semi-empirical model. Projected 90-year SLR for the upper limit A1FI scenario with enhanced glacier drawdown ranges from 0.56 to 1.01 m for islands with a measured range of vertical motion from −0.29 to +0.10 m. We classify tropical small islands into four broad groups comprising continental fragments, volcanic islands, near-atolls and atolls, and high carbonate islands including raised atolls. Because exposure to coastal forcing and hazards varies with island form, this provides a framework for consideration of vulnerability and adaptation strategies. Nevertheless, appropriate measures to adjust for climate change and to mitigate disaster risk depend on a place-based understanding of island landscapes and of processes operating in the coastal biophysical system of individual islands.
KeywordsVolcanic island Atoll Reef island Climate change Sea-level rise Disaster risk reduction
Fourth Assessment Report (IPCC)
Above sea level
El Niño-southern oscillation
Global mean sea level
Global navigation satellite systems
Global positioning system
International GNSS Service
Intergovernmental Panel on Climate Change
Mean sea level
North Atlantic oscillation
Special report on emission scenarios (IPCC)
Coastal vulnerability in small island developing states
Physical exposure and accelerated environmental change account for only part of the vulnerability of small islands. Challenges to sustainability can result from a broad spectrum of issues linked to demography and population density, health and well-being, culture and social cohesion, ecological integrity and subsistence resources, equity and access to capital, economic opportunity, basic services, technical capacity and critical infrastructure, among others. Many of the same issues apply to risk management and capacity for disaster risk reduction in small island states (Herrmann et al. 2004). Development pressures from these and other drivers compound the challenges of climate-change adaptation and risk reduction in small island states (Pelling and Uitto 2001). Efforts to enhance adaptive capacity and community resilience require a broad and holistic strategy and most likely a polycentric and multi-stakeholder approach (Ostrom 1999, 2010). Appropriate institutional, cultural, social, and policy mechanisms are required to support flexible and sustainable adaptation.
Within this framework, the geological, climatic, and oceanographic contexts are fundamental to the nature of exposure and key factors in managing adaptation to environmental change. Moreover, the impacts of climate change may first become apparent in major storms or other extreme events. Many years of development (sometimes with unrecognized maladaptation) may precede rare and catastrophic storms. The connection between extreme events and climate-change impacts points to the importance of physical vulnerability. Fundamental challenges in the management of coastal resources on many small islands include a scarcity of data and a lack of awareness of the natural processes and variability of coastal systems (Nunn et al. 1999; Lata and Nunn 2011). Realistic (data-backed) projections of future impacts (and associated uncertainties), greater understanding of coastal sediment dynamics, and strategies to enhance the natural function of reef and shore-zone biophysical systems are key prerequisites for robust adaptation.
Many economic functions on small islands are dependent on coastal access and resources. Tourist infrastructure is targeted predominantly to coastal sites, where inappropriate siting, design or management can augment vulnerability (Shaw et al. 2005). Critical port facilities are necessarily located at the coast and much port, road, and other infrastructure is vulnerable to damage from local or far-travelled tsunami, storm waves, or exceptional tides on anomalously high sea levels (Solomon and Forbes 1999; Jackson et al. 2005; Fritz et al. 2011; Donner 2012). In atolls, limited freshwater lenses and saltwater intrusion or contamination by rising sea levels or storms constrain development and limit agricultural production (Mimura et al. 2007).
Tropical small islands are bolstered by protective biological resources. It is widely recognized that coral reefs are the world’s largest coastal protection structures, but widespread degradation observed in many of the world’s reef systems can been attributed to a combination of climate and human impacts (Carilli et al. 2010; Harris et al. 2010; Perry et al. 2013). The importance of reef systems for coastal stability, as both protective structures and sediment incubators, as well as the many other ecosystem services they provide, underlines the need to promote reef health (McClanahan et al. 2002).
Accelerated SLR is one of the most pressing concerns of island residents, particularly the inhabitants of low-lying atolls. Large proportions of habitation and infrastructure are usually concentrated near the coast, even on high-relief islands, and the effects of future SLR, including impacts on reef systems and shoreline stability, are important. Communities occupying low-elevation coastal terraces on high islands are exposed to tsunami runup, storm waves, marine and river flooding, and erosion, but remain in exposed locations for a variety of cultural or economic reasons. Nevertheless, some communities have relocated to higher ground in response to severe impacts from SLR and coastal storms in former shorefront locations (Nunn et al. 1999).
Approach and methodology
This paper is largely a review, intended to highlight the biophysical settings and associated physical vulnerabilities that need to be considered in adaptation and sustainable development strategies for tropical and sub-tropical island communities. We propose a geomorphic classification of island types as a framework for assessing relative exposure to a range of coastal hazards. An exhaustive review of island conditions is beyond the scope of the paper, but we draw examples from our experience on Indian, Pacific, and Atlantic oceanic islands and islands in the Caribbean.
We address the science and data constraints for developing robust, island-specific projections of sea-level change. SLR integrates the effects of two major contributions: (1) changing ocean density with warming of the surface mixed layer of the ocean, and (2) addition of water to the ocean basins by melting of land-based ice (Church and White 2006; Cazenave and Llovel 2010). The regional distribution of SLR is determined in part by gravitational effects involving the relative proportions of meltwater from various regions and distances to source, as well as by large-scale ocean dynamics not considered here. Following Mitrovica et al. (2001) and James et al. (2011), we compute this so-called ‘fingerprinting’ component of future sea-level rise, which contributes to spatial variability. In general, for tropical islands remote from the poles, the fingerprinting may slightly enhance SLR. We then compute island-specific projections under various special report on emission scenarios (SRES) possible futures (Nakicenovic and Swart 2000; Nicholls et al. 2012) using projections of global mean SLR from the Fourth Assessment Report (AR4) of the Intergovernmental Panel on Climate Change (IPCC) (Meehl et al. 2007). We also consider an example of semi-empirical projections published since the AR4 (e.g., Rahmstorf 2007; Grinsted et al. 2009; Jevrejeva et al. 2010, 2012). We combine the resulting estimates with measurements of vertical land motion to estimate plausible ranges of future sea levels. We provide estimates for a representative set of 18 widely distributed island sites for which vertical motion is available. These computations are adjusted to 90 years to give the rise in mean sea level from 2010 to 2100.
Data on past sea levels are taken from the estimates of global mean sea level (GMSL) by Church et al. (2006) and more recently from satellite altimetry data, both of which are provided on-line by CSIRO (http://www.cmar.csiro.au/sealevel/index.html). Monthly and annual mean sea levels for island stations are obtained from the Permanent Service for Mean Sea Level (PSMSL) (Woodworth and Player 2003; http://www.psmsl.org/data/obtaining/) and other sources in the Caribbean (Sutherland et al. 2008). Data on vertical land motion are derived from global satellite navigation system (GNSS) stations using on-line records and velocity estimates, primarily from the Jet Propulsion Laboratory (JPL) (http://sideshow.jpl.nasa.gov/post/series.html).
Estimates of wave runup are derived from field observations by the authors and published data. Field surveys of coastal berms or beach ridges in Mahé and Praslin (Seychelles), Viti Levu (Fiji), Tarawa (Kiribati), and Aitutaki (Cook Islands) by Jackson et al. (2005), Forbes et al. (1995), Forbes and Biribo (1996) and Forbes (1995) respectively, were undertaken using graduated rods and horizon (adaptation of Emery 1961) or electronic total station methods and referenced in most cases to the reef flat, representing a low-water datum, and to local survey control. Surveys in the Seychelles were tied to global positioning system (GPS) control and the mean sea level (MSL) datum using post-processed static differential surveys and tidal records (Jackson et al. 2005).
Small island types and associated physical vulnerability
high volcanic islands (active or inactive), with fringing, emergent, or barrier reefs
near-atolls and atolls
emergent limestone islands including raised atolls
High volcanic islands
High volcanic islands are often surrounded by protective fringing or barrier reefs, which may enclose lagoons of varying size (Darwin 1842; Nunn 1994). Reef health and productivity may be compromised in such settings by the steep slopes and thick soils of high island interiors, where extreme rainfall can trigger high runoff, landslides, and debris flows (e.g., Harp et al. 2004). Larger islands may also have major rivers, creating flood hazards and delivering large quantities of sediment, which can dominate coastal morphology in the vicinity of their outlets (e.g., Mimura and Nunn 1998; Kostaschuk et al. 2001).
Near-atolls, atolls, and reef islands
Atolls lack an emergent volcanic core and are characterized by very low maximum elevations, limited land area, and thin freshwater lenses (McLean and Woodroffe 1994). With long-term subsidence typical of many atolls (Scott and Rotondo 1983), the volcanic peak is submerged and capped by limestone (Fig. 2). With fluctuating sea levels over glacial-interglacial cycles, most present-day atolls have been exposed subaerially during glacial lowstands, experiencing solution and denudation (Woodroffe 2002). Reefs are reactivated when sea levels rise again. Depending on rates of SLR and coral productivity, reefs may keep up with sea level, fall behind (becoming submerged), or catch up (if the rate of SLR diminishes or productivity increases) (Neumann and Macintyre 1985). The vertical growth potential of corals and coralline algal reef builders depends on a number of factors, but rates as high as 8 m/ka (metres per 1,000 years) have been reported from Mayotte Atoll in the Comoros, western Indian Ocean (Camoin et al. 1997) and 9–15 m/ka from the Caribbean (Adey 1978), although recent observations show a marked decline in some regions (e.g., Perry et al. 2013). The atolls and atoll reef islands observed today are geologically young features, having formed on older foundations since global sea level stabilized about 6,000 years ago (Bard et al. 1996). They have developed some degree of dynamic equilibrium with current climate and oceanographic environment, but are continually subject to readjustment, erosion and sedimentation, in response to varying sea levels, wind patterns, and storms.
High carbonate islands including raised atolls
High carbonate-capped islands (Fig. 2) occur in forearc belts adjacent to subduction zones such as the Tonga Trench (Clift et al. 1998; Dickinson et al. 1999), the Cayman Trench (Perfit and Heezen 1978; Jones et al. 1997), and the Lesser Antilles arc-trench system (Bouysse et al. 1990). Structural segmentation of the Tonga Ridge has led to varying rates of uplift, subsidence, or tilting affecting individual blocks and islands (Dickinson et al. 1999). The thickness of the carbonate cap in the Cayman Islands is unknown but exceeds 400 m (Emery and Milliman 1980). Like the islands of the Tonga Ridge, these are believed to be on different fault blocks moving independently (Horsfield 1975; Jones and Hunter 1990). Barbados is another carbonate-capped high island, formed on the Lesser Antilles accretionary prism at the leading (eastern) edge of the Caribbean plate (Bouysse et al. 1990). Other high islands with wide barrier reefs, including Rodrigues (Mauritius) and Bermuda, have cemented calcareous wind-blown sand deposits that form high cliffs on exposed coasts. These are not easily categorized, having elements of at least three island types.
Coastal hazards on small islands
The nature of the hazards, exposure and vulnerability—thus the most relevant adaptation measures—vary between island types in relation to elevation, but also to size, topography, bathymetry, lithology, reef morphology and ecological integrity, as well as human factors such as shore protection, or location and design of critical infrastructure and other property. The geographic region is important as it determines ocean climate (e.g., temperature and coral growth rate), storm climatology (including wind and wave patterns), and the regional trend of sea-level rise. Islands within ± 5° latitude about the equator are generally free of tropical cyclones, but occasional storm incursions, exceptional winds, or impacts of far-travelled swell from mid-latitude storms can cause significant damage, the effects of which are also influenced by sea-level variability resulting from El Niño-southern oscillation (ENSO) or other large-scale climate cycles. At tropical to mid-latitudes >5° (north or south), tropical cyclones are a major recurring threat (Hay and Mimura 2010). In addition to climate effects, geophysical hazards such as volcanic eruptions, landslides, earthquakes and tsunami require attention and may pose equal or greater risks to island communities.
Apart from catastrophic events, coastal stability is a function of wave energy, erodibility, and sediment supply, which may depend on reef health and the production of biogenic sand (Kench and Cowell 2001; Perry et al. 2008, 2011). Reefs represent not only a source of sediment, but play a major protective role, absorbing much of the deep-water wave energy. There is cause for concern about the mid-term fate of coral reefs (e.g., Hoegh-Guldberg et al. 2007), but recent work has shown that the coralline algae forming the resistant rims of some reefs may be more resistant to acidification than previously thought (Nash et al. 2013). In some places, exposure is mitigated and resistance to erosion increased where mangroves are present along the shore. Removal of mangroves can often be identified as a source of erosion problems in coastal communities (Mimura and Nunn 1998; Solomon and Forbes 1999).
Geological hazards: volcanoes, earthquakes, slope instability and tsunami
Low-lying communities on high islands with shallow coastal waters that promote tsunami shoaling may have relatively high exposure to far-travelled tsunami (Jackson et al. 2005). In contrast, small islands such as atolls on pinnacles rising from abyssal depths may derive some protection due to minimal shoaling. The Indian Ocean tsunami of December 2004 caused extensive damage on coastal terrace infrastructure in the high islands of the Seychelles. The shallow continental shelf promoted shoaling and refraction or diffraction to the back side of islands such as Mahé (Fig. 8b), while atolls of the southern Seychelles in deep water were largely unaffected (Shaw et al. 2005). Not all atolls in the Indian Ocean were thus protected. The same event inundated numerous atolls in the Maldive Islands, causing runup to 1.8 m MSL in South Maalhosmadulu Atoll (Kench et al. 2006). The location of this island on a broad carbonate bank with depths <500 m may have contributed to shoaling and exacerbated the impact. Elsewhere in the Maldives, overland flow depths up to 4 m were documented (Fritz et al. 2006).
The foregoing observations pertain to large-scale basin-crossing tsunami such as the 2004 event in the Indian Ocean or its 1833 equivalent (Zachariasen et al. 1999; Shaw et al. 2005). The 1755 Lisbon earthquake and a lesser event in 1761 are the only trans-oceanic tsunami reported in the Caribbean in the past 600 years (O’Loughlin and Lander 2003). On the other hand, regional and locally generated tsunami pose a critical threat to low-lying settlements and infrastructure in many island settings, particularly in the Caribbean, where of 85 recorded tsunami events since 1498, 17 have caused in total more than 15,000 human fatalities (Harbitz et al. 2012). Caribbean tsunami result from earthquakes along the Caribbean plate boundary, from related volcanic eruptions in the Lesser Antilles, and from onshore and submarine landslides. The highest tsunami in the region, resulting from an 1867 Virgin Islands earthquake, affected all the islands in the Lesser Antilles, with recently reassessed runup heights ranging up to 10 m (Harbitz et al. 2012). Slope instabilities on the flanks of active volcanic islands such as Tenerife in the Atlantic (e.g., Krastel et al. 2001) or La Réunion in the Indian Ocean (Oehler et al. 2008) constitute another major tsunami hazard and may result from dome or flank collapse, pyroclastic debris flows (lahars), or explosive submarine eruptions. There are 12 active volcanoes in the 10 major inner-arc islands of the Lesser Antilles and catastrophic flank collapse is a significant hazard (e.g., Boudon et al. 2007; Le Friant et al. 2006, 2009). Many island coasts in the Lesser Antilles have cliffs cut into volcano flank slopes—displacement of landslide blocks into the ocean is recognized as another major tsunami trigger. With the closely spaced islands in this region, tsunami travel times are short. Teeuw et al. (2009) estimate that up to 30,000 people on the south coast of Guadeloupe, 40–60 km to the north, are at risk from potential slope failure on Dominica. Locally generated tsunami are also recognized as a hazard in the Pacific, where coastal communities have been devastated by tsunami from nearby submarine slope failure (e.g., McAdoo et al. 2009). The 2009 Tonga Trench earthquake caused tsunami runup as high as 17 m in Samoa and 22 m in northern Tonga, causing 189 fatalities (Fritz et al. 2011).
Oceanographic hazards: waves and storm surges
Wave overtopping and ocean flooding are major hazards on low-lying atolls under storm conditions (Scoffin 1993). Tropical storm surges and waves can overwhelm island communities, as occurred at Manihiki (Fig. 5a), northern Cook Islands, during passage of Cyclone Martin in November 1997—only four houses were left standing in the two island villages and 20 residents were lost (de Scally 2008). Maragos et al. (1973) provide a graphic description of flooding and wave overtopping on Funafuti Atoll, Tuvalu, during Cyclone Bebe in October 1972.
Forbes (1996) and Solomon and Forbes (1999) described storm impacts from Cyclone Ofa in 1990 on the raised island of Niue (Fig. 7). Numerous facilities on top of coastal cliffs up to 25 m high were damaged severely by storm waves breaking against the cliffs. Many of these facilities were repaired, only to be damaged even more severely by category 5 Cyclone Heta 14 years later. Thus, while raised atolls are largely immune to storm flooding, their narrow reef fringe, allowing deep-water waves to break almost directly against the cliffs, exposes cliff-top infrastructure and properties to extraordinary wave impact.
Sea-level rise and variability
Atolls and the low-lying terraces of high islands are susceptible to more frequent or higher flooding under climate-induced acceleration of global mean SLR. Deepening of water over reefs may increase wave energy at the shoreline and salt water may intrude into island soils and aquifers. Sea-level variability due to ENSO or other large-scale circulation, as well as tides and storm surges, all ride on the MSL. Thus it is important to develop robust projections of local SLR for individual regions and islands. These require knowledge of the global drivers as well as local factors such as uplift or subsidence rates. There is a growing consensus that the SLR projections of the IPCC (2007) AR4 were conservative and that SLR this century is likely to exceed AR4 estimates (Rahmstorf et al. 2007; Rahmstorf 2010; Church and White 2011). Post-AR4 projections of twenty-first century global mean SLR range up to 1.4 m or more but less than 2 m (Rahmstorf 2007, 2010; Pfeffer et al. 2008; Grinsted et al. 2009; Jevrejeva et al. 2010, 2012; Rahmstorf et al. 2012b).
Church et al. (2004, 2008), Church and White (2006, 2011), Domingues et al. (2008), Jevrejeva et al. (2008), Cazenave and Llovel (2010) and others have documented the slow rise of GMSL since the nineteenth century, slow or intermittent acceleration through the twentieth century, and more rapid acceleration over the past two decades. Meanwhile, satellite altimetry over the ocean basins since 1993 has revolutionized the monitoring of GMSL (Leuliette et al. 2004), showing an upward trend well correlated with the tide-gauge reconstruction that suggests an acceleration to 3.2 ± 0.4 mm year−1 (1993–2009) from the mean rate of 1.9 ± 0.4 mm year−1 since 1961 (Church and White 2011).
the range of emission scenarios and associated global sea-level projections in the most recent IPCC report—the AR4 at the time of writing (Meehl et al. 2007);
remaining uncertainties in the spatial distribution of future sea-level change (a function of uncertainties in the relative contributions of the Greenland and Antarctic ice sheets, large ice caps and mountain glaciers in various regions);
poorly constrained changes in ocean circulation or changes in the intensity of ENSO, NAO, or other large-scale oscillations that can influence regional sea levels;
limited data (absent for many islands) on rates of vertical land motion and large uncertainties where the geodetic time series are short (Table 1).
Ninety-year projections (2010–2100) of relative sea-level rise (SLR) for 18 selected island sites in the Indian, Pacific, and Atlantic Oceans together with measurements of local vertical crustal motion (VM) and uncertainty (±1sVM) on crustal motion (all in meters over 90 years) B1MIN and A1FIMAX are the minimum and maximum projections from the IPCC (2007) and A1FIMAX+ is the upper limit for the A1FI SRES scenario augmented to account for accelerated drawdown of ice sheets (Meehl et al. 2007)
Port Louis (Mauritius)
Diego Garcia (UK)
Guam (United States)
Majuro (Marshall Islands)
Rarotonga (Cook Islands)
West End (Bahamas)
St. Croix (US Virgin Islands)
Grande Rivière [Trinidad and Tobago]
GMSL has been tracking close to the upper limit of the IPCC (2007) projections over the past decade and more (Fig. 10) (Rahmstorf et al. 2007, 2012a). This suggests that the B1 scenario lower-limit projections (Table 1; Fig. 11) severely underestimate future sea levels, as they are comparable to the late twentieth century mean SLR prior to the more recent acceleration. Figure 11 also shows the upper limit projections for the fossil-fuel intensive A1FI scenario, both without (A1FIMAX) and with (A1FIMAX+) the contribution of accelerated glacier outflow from the major ice sheets (Meehl et al. 2007). It also shows the range of a semi-empirical projection derived from Rahmstorf (2007) and Grinsted et al. (2009), equivalent to 1.15 m globally over 90 years (James et al. 2011), for various meltwater source scenarios (RGMIN to RGMAX). These projections incorporate observed trends and uncertainty in vertical crustal motion (Table 1; Fig. 11 grey bars with error bars). Using these scenarios, we see that the projected MSL changes over the 90 years 2010–2100 have ranges of 3–43 cm (B1MIN), 39–80 cm (A1FIMAX), and 56–101 cm (A1FIMAX+) for the islands considered here (Fig. 1). However the uncertainty in vertical motion translates to uncertainties in these SLR projections ranging from 5 to 67 cm (Table 1). For the semi-empirical model, the highest local projections (RGMAX) have a range of 106–156 cm (Table 1). A large part of the variability between sites is a function of vertical motion, although the redistribution of meltwater in the oceans (‘sea-level fingerprinting’) also contributes.
Island vulnerability to sea-level rise and storms
Much of the concern about accelerating SLR centers on the question of whether reef islands on atolls will be lost through erosion and flooding in future decades. The low elevation of atoll islands and their resident communities is a serious constraint. The area higher than 2 (3) m MSL accounts for 34 % (7 %) of total land area in the Gilberts (Kiribati) and Tuvalu, 33 % (8 %) in the Cocos (Keeling) Islands, 28 % (7 %) in Diego Garcia, and only 4 % (1 %) in the Maldives (Woodroffe 2008). In general, low atoll elevations facilitate inundation by SLR and flooding by extreme tides, anomalous high water episodes (e.g., El Niño), and storms (Maragos et al. 1973; Yamano et al. 2007; Donner 2012). As discussed above, wave energy on reef island shores is limited by energy loss at the outer reef and controlled by depth over the reef rim and flat. It follows that rising sea levels may produce higher wave energy at reef-island shores, which could lead either to erosion or island washover and aggradation. Recent evidence points to the dynamic resilience of reef islands in the face of twentieth century SLR, as sediment is retained within the atoll and erosion on one part of a reef island may be largely balanced by deposition on another part (Webb and Kench 2010). It is also clear that, with a positive sediment budget, reef islands can accrete on the ocean side as sediment from the reef rim is transported onshore (Woodroffe et al. 2007; Woodroffe 2008; Perry et al. 2011). Atolls such as Nonouti (Fig. 5b), with numerous passages from the reef flat to the lagoon through inter-islet channels, may see a large proportion of sediment production from the reef transferred to the lagoon or alongshore off the end of the islet-chain (Forbes and Biribo 1996). This may contribute to erosion of ocean-side shores in some sectors. Therefore, although reef islands may aggrade through wave runup and overtopping so long as vertical growth of the reef can keep pace with future SLR, the specific response of individual atolls and islets within atolls will depend to a large extent on the local morphodynamics. Wave overtopping events damage infrastructure and create safety concerns, but can gradually raise island elevations, unless blocked by shore protection structures (Kench 2012).
A key question is the vertical growth potential of the reef, which may be diminished by elevated temperatures, ocean acidity, pollution and nutrient enrichment, sediment influx or resuspension, physical disruption by major storms or human activities, or excessive exploitation of key species (Smith and Buddemeier 1992; Hoegh-Guldberg et al. 2007; Perry et al. 2011, 2013). The morphology and species composition of the reef, wave energy, nutrient flux, and depth are all factors that affect the vertical growth rate (Adey 1978; Chappell 1980; Woodroffe 2002). There is new evidence to suggest that rapid reef accretion can occur with high terrigenous sediment input (Perry et al. 2012) but reef health and biodiversity may be compromised. Beyond the physical and biological status of the reef, there is a need to understand the limitations on productivity of other key island sediment constituents, notably foraminifera in the Pacific and Halimeda in the Caribbean (McClanahan et al. 2002; Yamano et al. 2005).
The habitability of low-lying atolls and reef islands is critically dependent on the availability of fresh water. Freshwater aquifers on reef islands are shallow lenses overlying brackish and saline water. Shoreline changes, particularly erosion and loss of island area, can negatively affect the freshwater lens and saline contamination can occur when major storms overflow island communities (Maragos et al. 1973; Solomon 1997). Under these circumstances, saltwater can flow into open wells and percolate directly into the highly permeable island soils. Much work has been done on the engineering of freshwater systems and assessment of freshwater demand, but a full understanding of water vulnerability under climate change or catastrophic storms is lacking for many islands (e.g., Schwerdtner Máñez et al. 2012).
This review demonstrates that tropical small islands are subject to a wide range of physical forcing and that island shoreline stability is dependent in large part on the maintenance of healthy coastal ecosystems. The range of coastal hazards identified here highlights the substantial exposure of some island communities. At the same time, it is clear that coral growth, biogenic sediment production, and wave action can serve to maintain stability and even contribute to island growth, this being the way in which reef islands were formed in the first place. Thus it is clear that development and adaptation strategies (e.g., ecosystem-based adaptation) designed to complement natural resilience in the coastal system should have a higher probability of success. This approach presupposes an understanding of the relevant coastal sedimentary and ecological processes of interest, which highlights the importance of biophysical science as one component of the information package needed for effective coastal management, climate-change adaptation, and disaster risk reduction. In a broader governance context, it is recognized that understanding of key processes forms an essential foundation for sustainable development (Glaser et al. 2012).
Effective disaster risk reduction also requires knowledge of potential threats. In some cases, for rare and exceptional events such as major tsunami or extreme storms, there may be some residual community memory, but often there is not. Effective stakeholder collaboration and attention to local and traditional knowledge are important and may identify issues that would otherwise be overlooked. There is a large and growing literature on the value of indigenous knowledge and protocols for integrating locally sourced information with other forms of knowledge including western scientific approaches (e.g., Crump and Kelman 2009; Kelman and West 2009; McAdoo et al. 2009; Mercer et al. 2009). The explosive growth of social media, even in remote communities, opens up new possibilities for information exchange and participatory dialogue. New tools are being developed to invite and enable contributions of information from the wider public (e.g., Tienaah 2011; Nichols et al. 2011).
The island typology can provide a template (checklist) of potential hazards and the nature of potential impacts, but our review has highlighted the critical importance of local place-based analysis of the coastal biophysical and social-ecological systems. Understanding shoreline stability on atoll islands and projecting long-term land availability under various climate-change scenarios requires detailed data on coastal morphology, including high-resolution digital elevation models, and on the processes that drive coastal change. In this context, Woodroffe (2008) pointed to a number of specific knowledge requirements. He noted the need to watch for thresholds that might lead to major transformations in the nature and stability of reef and shore systems. Webb and Kench (2010), reporting an analysis of multi-decadal island shoreline change, concluded that “island nations must place a high priority on resolving the precise styles and rates of change that will occur over the next century and reconsider the implications for adaptation”. In another context, evaluating the stability and size of potential tsunami-generating landslide blocks on heavily forested volcanic island slopes in Dominica, Teeuw et al. (2009) identified mapping with suitable tools as a prime requirement.
Other critical data needs have also emerged from this study. It is evident that measurements of vertical crustal motion are a prerequisite for robust projections of future sea levels at any specific island site (Fig. 11). Long-term water level records from tide gauges are equally important, even when complemented by satellite altimetry (Davis et al. 2012). Yet the network of GNSS stations on islands worldwide is extremely sparse and the number of co-located GNSS and tide gauges is even smaller. Even where data are available, as at many of the 18 sites used for SLR projections in this study (Fig. 1), continuity is a challenge and very few islands are represented in the active network of the International GNSS Service (http://www.igs.org/network/netindex.html).
Realistic physical hazard and impact projections are a prerequisite for effective adaptation planning. The hazard mix and severity may vary with island type and regional setting. There is a need for monitoring of evolving physical exposure to provide objective data on island responses and early warning of changing risk. Reef islands may be resilient under rising sea level, at least at rates experienced during the twentieth century, maintaining island area but not necessarily fixed shoreline positions. The latter has implications for land ownership, property boundaries, and shorefront infrastructure. Coastal stability requires maintenance of healthy coastal ecosystems, particularly in tropical regions where organisms produce sand. Degradation of protective reefs will increase exposure to erosion. Effective adaptation to SLR requires realistic projections, which need to incorporate the latest climate science, knowledge of vertical motion, regional ocean dynamics, and meltwater redistribution in the oceans. A precautionary approach requires robust island-specific projections of the full range of potential sea-level scenarios and future updating as new insights and consensus develop through the coming decade and beyond. Ultimately there is a need for place-based studies incorporating objective science and indigenous knowledge to build an understanding of the specific processes operating in each island system.
This study incorporates our combined experience on tropical small islands in many parts of the world and would not have been possible without generous financial support from a wide range of agencies. Our current collaboration is supported by the C-Change International Community-University Research Alliance (ICURA) co-funded by the Social Sciences and Humanities Research Council and the International Development Research Centre. Our past work has been supported by the Canadian International Development Agency, the Japan International Cooperation Agency, the South Pacific Applied Geoscience Commission (SOPAC), and the Geological Survey of Canada (GSC) (Natural Resources Canada), among others. We are grateful to Andrea Darlington (University of Victoria and GSC) for assistance with the SLR projections, to Gavin Manson and Paul Fraser (GSC) for advice on mapping issues, to Dick Pickrill (GSC retired) for his unstinting support of our South Pacific collaboration in the 1990s, and not least to our late colleague Steve Solomon (GSC and SOPAC), who applied his singular skills and insight to the study of Arctic coasts and tropical small islands. We are grateful to Vaughn Barrie and John Shaw (both GSC) and two anonymous journal reviewers for helpful comments on an earlier draft. This is a contribution to LOICZ (Land–Ocean Interactions in the Coastal Zone) and is contribution no. 20120460 of the Earth Sciences Sector (Natural Resources Canada). ©Canadian Crown Copyright reserved 2013.
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