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The coast is one of the most dynamic environments on Earth, shaped by the constant interaction of marine, atmospheric and terrestrial processes. At A-Level, AQA requires you to understand the coastline through the lens of systems theory — treating the coast as an open system with inputs, outputs, stores and transfers of energy and materials. This approach, rooted in General Systems Theory developed by Ludwig von Bertalanffy (1968), allows geographers to analyse how coastal landscapes change over time and space.
A system is a set of interrelated components that work together as a complex whole. In geography, we distinguish between three types of system:
| System Type | Characteristics | Coastal Example |
|---|---|---|
| Open system | Exchanges both energy and matter with its surroundings | A beach receiving sediment from rivers and losing it to longshore drift |
| Closed system | Exchanges energy but not matter | The global sediment budget (theoretical) |
| Isolated system | No exchange of energy or matter | Does not exist in nature |
The coast is fundamentally an open system. It receives energy from waves, wind and tides, and matter in the form of sediment from rivers, cliff erosion and offshore sources. It loses energy through friction and wave breaking, and matter through sediment transport beyond the system boundary.
Key Definition: A coastal system is an open system in which inputs of energy and sediment are processed through a series of stores and transfers, producing outputs that shape the coastal landscape.
Inputs are the driving forces that provide energy and material to the coast:
Outputs represent the energy and material that leave the system:
Within the coastal system, energy and material are temporarily held in stores (also called components or sinks) and moved between them by transfers (also called flows or processes):
| Store | Description |
|---|---|
| Beaches | Accumulations of sand, shingle or pebbles between low and high water marks |
| Sand dunes | Aeolian deposits of sand stabilised by vegetation |
| Mudflats and salt marshes | Fine sediment deposited in sheltered intertidal areas |
| Cliffs | Rock faces that act as a store of potential sediment |
| Offshore bars | Submerged ridges of sediment parallel to the coast |
| Spits and bars | Elongated deposits of sediment formed by longshore drift |
One of the most important applications of systems theory to the coast is the sediment cell (also called a littoral cell). This concept was formalised in the UK by Motyka and Brampton (1993) for the Ministry of Agriculture, Fisheries and Food (MAFF).
Key Definition: A sediment cell is a largely self-contained stretch of coastline within which the movement of sediment is essentially a closed system — sediment is recycled within the cell with minimal exchange across its boundaries.
graph TD
subgraph "Sediment Cell Model"
A["Inputs: cliff erosion, rivers, offshore"] --> B["Beach Store"]
B --> C["Longshore Drift Transfer"]
C --> D["Spit / Bar Store"]
D --> E["Outputs: deep water loss"]
B --> F["Dune Store"]
F --> B
C --> B
end
The coastline of England and Wales has been divided into 11 major sediment cells and 55 sub-cells. The boundaries between cells typically occur at major headlands, estuary mouths or stretches of deep water where sediment transport is negligible.
| Cell Number | Location | Approximate Length |
|---|---|---|
| 1 | St Abb's Head to Flamborough Head | 300 km |
| 2 | Flamborough Head to The Wash | 200 km |
| 3 | The Wash to Thames Estuary | 190 km |
| 4 | Thames Estuary to Selsey Bill | 200 km |
| 5 | Selsey Bill to Portland Bill | 170 km |
| 6 | Portland Bill to Land's End | 350 km |
| 7 | Land's End to Hartland Point | 330 km |
| 8 | Hartland Point to St David's Head | 420 km |
| 9 | St David's Head to Great Orme | 330 km |
| 10 | Great Orme to Solway Firth | 370 km |
| 11 | Solway Firth to St Abb's Head | 560 km |
Each sediment cell has a sediment budget — the balance between inputs and outputs:
Exam Tip: Questions on sediment cells often ask you to explain how human intervention in one part of a cell can disrupt the sediment budget elsewhere. A classic example is how groynes at Mappleton on the Holderness coast starved beaches downdrift at Cowden of sediment, accelerating erosion there from 1.8 m/year to over 4 m/year after the scheme was completed in 1991.
The littoral zone is the area of coastline directly influenced by marine processes. It can be subdivided:
| Zone | Location | Key Processes |
|---|---|---|
| Backshore | Above the normal high tide mark, reached only by storm waves | Aeolian processes, weathering, mass movement |
| Foreshore | Between normal high and low tide marks (the intertidal zone) | Wave action, tidal processes, erosion and deposition |
| Nearshore | From low tide mark to the point where waves begin to break | Wave shoaling, longshore currents |
| Offshore | Beyond the wave base where waves do not affect the sea bed | Minimal direct coastal processes |
Understanding these zones is critical because different processes dominate in each, producing distinct landforms and deposits.
Coastal systems tend towards a state of dynamic equilibrium — a condition where the system is constantly adjusting to maintain a balance between inputs and outputs. This does not mean the coast is static; rather, it fluctuates around an average condition.
Two types of feedback operate in coastal systems:
Negative feedback (self-regulating): A change triggers a response that counteracts the original change, returning the system towards equilibrium.
Example: Storm waves erode a beach, moving sediment offshore to form a bar. The bar causes waves to break further from the shore, reducing their erosive power. Constructive waves then gradually return sediment to the beach.
Positive feedback (self-reinforcing): A change triggers further change in the same direction, pushing the system away from equilibrium.
Example: Cliff erosion removes vegetation from the cliff top, which reduces interception and infiltration, increasing surface runoff. This accelerates further erosion through gullying and mass movement. The cliff retreats faster and faster until a new equilibrium is established.
graph LR
subgraph "Negative Feedback"
A1["Storm removes beach sediment"] --> B1["Offshore bar forms"]
B1 --> C1["Waves break further out"]
C1 --> D1["Reduced erosion at beach"]
D1 --> E1["Beach rebuilds"]
end
graph LR
subgraph "Positive Feedback"
A2["Cliff erosion"] --> B2["Vegetation lost"]
B2 --> C2["Increased runoff"]
C2 --> D2["Accelerated erosion"]
D2 --> A2
end
Coastal processes and changes operate across multiple scales, and the AQA specification requires understanding of this:
| Scale | Time Period | Examples |
|---|---|---|
| Short-term | Hours to days | Individual storm events, tidal cycles |
| Medium-term | Years to decades | Seasonal beach profiles, cliff retreat rates |
| Long-term | Centuries to millennia | Sea level change, isostatic adjustment, coastal evolution |
| Geological | Millions of years | Formation of coastlines, lithological change |
| Scale | Area | Examples |
|---|---|---|
| Micro | Individual landform | A single rock pool, a blow hole |
| Meso | Section of coast | A bay, a spit, a beach |
| Macro | Regional | A sediment cell, the Holderness coast |
| Mega | Continental/global | Global sea level patterns, plate tectonics |
Exam Tip: In extended answer questions on coastal systems, explicitly reference the temporal and spatial scales at which processes operate. This demonstrates synoptic understanding and is rewarded in the AO2 marks for application. For example, note that while a storm event (short-term, micro-scale) may destroy a section of beach, the sediment budget of the wider cell (long-term, macro-scale) may remain in equilibrium.
| Strengths | Limitations |
|---|---|
| Provides a holistic framework for understanding coastal change | Over-simplifies complex, chaotic natural processes |
| Helps identify cause-and-effect relationships | Sediment cell boundaries are not truly closed — leakage occurs |
| Useful for coastal management planning and decision-making | Difficult to measure all inputs and outputs accurately |
| Allows prediction of consequences of human intervention | Does not fully account for episodic, high-magnitude events |
| Widely accepted by researchers and policymakers (e.g., DEFRA, Environment Agency) | Human activity often disrupts natural system operation |
The systems approach remains the dominant framework used in UK coastal management, underpinning Shoreline Management Plans (SMPs) introduced from 1995 onwards. Despite its limitations, it provides an essential tool for understanding and managing one of the world's most dynamic environments.