The term ‘dynamics’ is taken here to reflect both internal dynamics (changes occurring within a habitat due to internal or external forces, where the habitat itself remains identifiable) as well as profound changes in the nature of a habitat leading to a transition into another type. The latter could be cyclic, reversible or irreversible. Changes within a habitat could be gradual species replacement in a benthic macrofauna community as a result of colonisation from the south during prolonged periods of higher mean annual water temperatures. Also, shifts to shorter-lived species in response to more frequent disturbance by bottom trawling fishing vessels are well-established examples (e.g. Frid et al., 2000). Transition of one habitat into another could be due to gradual succession, such as occurring on salt marshes that accrete with positive sediment trapping (Leendertse et al., 1997, Lefeuvre & Bouchard, 2002). Cyclic habitat transitions can be illustrated by the accretion-erosion cycle associated with moving sand dunes, above as well as below water (e.g. Marbà & Duarte, 1995).
Accretion
The accumulation of (beach) sediment, deposited by natural fluid flow processes.
See Glossary for a complete list of all terms. |
Natural, internal dynamics are coupled to physical forcing and occur at a range of temporal scales. The tides, for example, cause substantial, predictable changes in environmental conditions over ~6 – 24 hours, i.e. within a day, but also longer periods occur. Next, all across Europe distinct seasonality is apparent in coastal waters and on land. Seasonality, from an ecological perspective, is fairly well predictable with day length, light availability and/or temperature (e.g. Vermaat & Verhagen, 1996, Marba et al., 1996). Climate change, however, may lead to an uncoupling of physical forcing and biotic responses (Phillipart et al,. 2003). Thirdly, at larger temporal scales, weather patterns change between years and generate highly variable sequences of comparatively dry, wet, warm or cold years, the North Atlantic Oscillation being an important underlying forcing factor. Variation at all these three scales has profound, nested, impacts on the functioning of coastal ecosystems, and hence on the communities of living biota populating coastal habitats. A substantial European research effort has been invested in better understanding these natural dynamics of coastal ecosystems.
North Atlantic Oscillation (NAO)
The NAO is a large-scale fluctuation in atmospheric pressure between the subtropical high pressure system located near the Azores in the Atlantic Ocean and the sub-polar low pressure system near Iceland and is quantified in the NAO Index. The surface pressure drives surface winds and wintertime storms from west to east across the North Atlantic affecting climate from New England to western Europe as far eastward as central Siberia and eastern Mediterranean and southward to West Africa.
See Glossary for a complete list of all terms. |
Transitional dynamics, or a change into another type of habitat, is probably the result of a substantial change in forcing factors, whether abiotic or biotic. The growing body of literature on resilience of ecosystems coupled to positive feedbacks and alternative stable states (e.g. Van de Koppel et al., 2001), suggests that also the accumulation of individually small changes may lead to a drastic change in ecosystem state, or, a transition from one habitat type to another. Examples of habitat transitions are the drastic declines in seagrass beds across Europe (e.g. Giesen et al., 1990, Frederiksen et al., 2004a) We will summarise both types of dynamics briefly here (Table 3) and have merged several habitats that appear to co-occur. Mobile sediment may generate apparently cyclic transitions between different habitats, both on land and in the sea. Rare, extreme events, such as heavy storms and seismic movements of the earth crust may cause considerable change in coastal habitats due to massive, incidental relocations of sediment. Particularly in the Mediterranean, seismic incidents are sufficiently frequent over longer time scales to be taken into consideration. Because of the erratic, unpredictable outcome in terms of habitat dynamics, seismic events have not been incorporated into Table 3. Isostatic sea level rise as well as coastal subsidence are additional natural processes leading to gradual or abrupt transitions in coastal habitats. Succession in shore meadows of the Northeastern Baltic are a good example. Climate change effects will be discussed later. |
| Habitat type |
Dynamics |
|
| |
Within habitat |
Transitions between habitats |
| Cliffs, shingle beaches, kelp beds |
T,S,A |
Erosion; colonisation by vegetation; changes in macroalgal abundance of kelp with altered foodweb structure; CWC for shingle |
| Wetlands and dune complexes* |
T,S,A |
CPH |
| Salt marsh* |
T,S,A |
CPH, passing mobile dunes may alter vegetation |
| Sand-banks and mudflats* |
T,S,A |
CWC; CPH |
| Seagrass beds* |
T,S,A |
CWC; increased turbidity will decrease depth penetration; stronger hydrodynamics will lead to an increased fragmentation of the canopy |
| Lagoons |
S, A |
Sedimentation may lead to infilling; possibly peat formation; fracture of the barrier to the sea will disrupt the quiet lagoonal conditions; may be coupled to changes in barrier-disturbing storm frequencies |
| Subtidal sediments |
S, A |
Changes in composition of detritus rain from pelagic or coast may affect benthic fauna and fish; deep currents may change course |
| Open sea pelagic |
S, A |
Water temperature, nutrient loading gradients and turbulence spectra may lead to altered plankton and fish community composition |
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