Patterns in Sandy Beach Macrofauna 3

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Patterns in Sandy Beach Macrofauna 3 MARINE ECOLOGY PROGRESS SERIES Vol. 295: 1–20, 2005 Published June 23 Mar Ecol Prog Ser FEATURE ARTICLE: REVIEW Patterns, processes and regulatory mechanisms in sandy beach macrofauna: a multi-scale analysis Omar Defeo1,*, Anton McLachlan2 1Centro de Investigación y de Estudios Avanzados del IPN, AP 73 Cordemex, 97310 Mérida, Yucatán, México 2College of Agricultural and Marine Sciences, Sultan Qaboos University, Oman ABSTRACT: Physical and biological factors govern com- munity and population features of sandy beach macro- fauna. At the macroscale, species richness decreases from tropical to temperate beaches, and from macrotidal dissipative to microtidal reflective beaches. At the species level, life history traits are highly plastic over latitudinal gradients; large-scale variations in environmental vari- ables modulate intraspecific phenotypic differentiation. At the mesoscale, alongshore and across-shore distribu- tions tend to be unimodal, bell-shaped within a beach, with abundance varying from the central region to the boundaries, even though environmental gradients (wave exposure, salinity) can cause asymmetries. Zona- tion is highly dynamic and not sharply defined. This is attributed to short- (hourly, daily) or medium- (seasonal) term reactions to environmental conditions, passive transport and sorting by the swash (e.g. recruits), active micro-habitat selection (e.g. adults), and intra- and inter- Sandy beaches are defined by just 3 factors—tide regime, sand specific interactions. Across-shore distribution may be- particle size and wave energy—and occur as a range from come multimodal due to intraspecific segregation by reflective (upper) to dissipative (lower) types. Since macrofauna sizes during recruitment. At the microscale (individual show clear patterns of response to beach type, these simple neighbourhood or quadrat scale), behavioural factors and environments provide a unique opportunity to explore processes intra-/interspecific interactions become more important controlling community and population ecology. Photos by Dr. Andrew Short (University of Sydney, Australia) as density increases. Human induced impacts also gener- ate variability in population demography, structure and dynamics. We identify physical-biological coupling at dif- KEY WORDS: Sandy beaches · Macrofauna · Commu- ferent temporal and spatial scales, emphasizing the role nities · Populations · Patterns · Regulation · Processes of life history traits in order to assess alternative regula- Resale or republication not permitted without tory mechanisms and processes. Our synthesis suggests written consent of the publisher that: (1) biological interactions are more important regu- latory agents than previously thought: in benign dissipa- tive beaches or undisturbed sites, intra- and interspecific INTRODUCTION competition can be more intense than in reflective beach- es or disturbed sites, where the populations are physi- cally controlled; (2) supralittoral forms are relatively inde- At the time of the first international sandy beach pendent of the swash regime and show no clear response symposium in 1983, sandy beach research was in a to beach type; (3) marked long-term fluctuations are transition from early, mainly qualitative studies of noticeable in species with planktonic larvae structured as macrofauna ecology and ecophysiology, to quantita- metapopulations, due to environmental disturbances and tive work (McLachlan & Erasmus 1983). Studies on stochasticity in reproduction and recruitment. energy flow and nutrient cycling in beach ecosystems *Email: [email protected] © Inter-Research 2005 · www.int-res.com 2 Mar Ecol Prog Ser 295: 1–20, 2005 Dean’s parameter ⍀ produce a range of beach morphody- 0 25 10 namic types which span a continuum 0 from microtidal reflective beaches, Reflective I Dissipative narrow and steep, to macrotidal dis- n sipative systems, which are wide and t flat, and under conditions of large e tides, grade into tidal flats (for review 0 100 r 0 300 see Short 1996). The most accretional Beach width (m) m Beach width (m) state is the reflective beach, formed 3 e under condition of small tides and Low tide terraced Ultra-dissipative waves and coarse sand; here there i is no surf zone and wave energy is a reflected back to sea from waves t breaking directly on the steep beach e face. In erosional or dissipative 0Beach width (m) 300 Beach width (m) 15 0 600 states the beach is flat and fronted by a wide surf zone, in which waves Fig. 1. Beach classification based on 2 composite indices developed for sandy shores: Dean’s parameter (Ω) and the Relative Tide Range. Dissipative, inter- dissipate much of their energy. The mediate and reflective domains are defined for microtidal open beaches where dissipative state forms under condi- tide range <2 m (after Short 1996) tions of large tide range, high wave energy, fine sand, and tends to be more prevalent at higher latitudes. A remained a dominant theme through the 1980s. In the series of intermediate states are recognized between 1990s most sandy beach research focused on commu- the above extremes (Fig. 1). nity and population ecology. Beach research lagged far Various indices of beach type have been used by behind studies of other coastal environments, and ecologists. Dean’s dimensionless fall velocity (Ω), a before 1980 it lacked a body of theory to drive it, but measure of how reflective or dissipative a microtidal this has steadily changed. Although they are still less beach is (Short 1996), is defined as: studied than most other coastal systems, beaches are much better characterized in the new millennium. A Ω= Hb ⋅ significant body of knowledge has accumulated and a Ws T variety of hypotheses concerning sandy beach ecosys- where Hb is breaker height (m), Ws is sand fall veloc- tems and communities have been developed, so that ity (m s–1) and T is wave period (s). Ω < 2 characterizes beach studies have become increasingly theory driven. reflective beaches, whereas Ω > 5 defines dissipative In this review we summarize the current status of ones and 2 < Ω < 5 characterizes intermediate beach community and population ecology for sandy beach states (Fig. 1). Essentially, Ω is a measure of the ability macrofauna (hyperbenthos not included), focusing on of the prevalent wave energy to erode sand. Another key processes operating at different scales, and on measure of beach type is relative tide range RTR = how they interact to yield the patterns observed. TR/Hb, where TR is spring tide range (m). RTR indi- We also refine the theory, identifying the physical- cates the relative importance of tides versus waves in biological coupling at different temporal and spatial controlling beach morphodynamics (Fig. 1). As Ω does scales and emphasising the role of life history traits in not take tides into account, the Beach State Index (BSI) order to assess the magnitude of alternative regulatory has been used to compare beaches subject to differing mechanisms. tide ranges; BSI is Ω multiplied by tide range and indicates the ability of waves and tides to move sand (McLachlan et al. 1993). Soares (2003) developed the THE BEACH ENVIRONMENT Beach Deposit Index (BDI), a composite index of beach slope and grain size. Recently, McLachlan & Dorvlo The benthic macrofauna of sandy beaches includes (2005) developed the beach index (BI): representatives of many phyla, but crustaceans, mol- ⎛ ⋅ ⎞ luscs and polychaetes are usually dominant and can be = ⎜ Mz TR ⎟ BI log10 ⎝ ⎠ divided into intertidal and supralittoral forms (Brown & S McLachlan 1990). Their habitat is dynamic and defined where Mz is the mean grain size (in phi units + 1, to by 3 factors: tides, waves and sand. The interactions be- avoid negative values), TR is the maximum spring tide tween tidal regime, wave climate and sediment type range (m) and S is beach face slope (dimensionless). Defeo & McLachlan: Patterns in sandy beach macrofauna 3 Water movement over the beach face, Temperate Low Species richness Biomass: g·m-1 after a broken wave (bore) collapses on High the sand, is termed swash (McArdle & Warm McLachlan 1991, 1992). In reflective temperate beaches, waves break directly on the beach face generating harsh swash cli- Sub- mates, i.e. dynamic, turbulent swashes tropical with short periods, with many swashes Latitude running above the sand water saturation level, and water draining rapidly into the Tropical High Low coarse sand. Conversely, dissipative sys- 0 R I DUDTF 4 0 R I DUD TF 4 tems have benign swashes, where much Beach Index Beach Index of the wave energy is consumed in the surf zone so that swashes reaching the Fig. 2. Conceptual model of latitudinal variations in species richness (number –1 beach face tend to be less turbulent and of species per transect survey) and biomass (g m ) as a function of beach type, as categorized by the Beach Index. The number of species increases at low have longer periods; swashes seldom latitudes under conditions of (1) fine sands and flatter slopes, (2) benign swash go above the saturated beach face so climates, and (3) increasing tide range. Biomass is also highest towards tidal there is little drainage into the sand (Mc- flats and increases from tropical to temperate sandy beaches (R = reflective, Lachlan & Turner 1994). Sandy beach I = intermediate, D = dissipative, UD = ultradissipative, TF = tidal flat) macrofauna experience this environ- ment through 3 suites of physical factors: the sediment texture and movement, the swash cli- ical to elucidate these large patterns; tropical regions mate, and the exposure/moisture gradient on the beach had a greater proportion of reflective beaches than face (Brown & McLachlan 1990). Sediment texture and subtropical or temperate regions, the latter being movement includes particle size, sorting, fluidity and dominated by dissipative beaches because of higher accretion/erosion dynamics. Swash climate includes wave energy and fine sand (Soares 2003, McLachlan & the swash period, speed, turbulence and water move- Dorvlo 2005). ment over and into the beach face. The intertidal Following the opposite trend, abundance and biomass gradient is the degree of aerial exposure of the sedi- increase from tropical to temperate beaches (Fig.
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