Explain the physical and human challenges affecting coastal environments, evaluate the range of management strategies used to address these challenges, and assess their effectiveness using appropriate criteria.
| Landform | Dominant process | Typical setting | Key features |
|---|---|---|---|
| Cliffs & wave‑cut platforms | Erosion (hydraulic action, abrasion, solution) | High‑energy coast, resistant rock | Steep face, flat platform at base, measurable retreat rate |
| Caves, arches, stacks | Erosion + differential weathering | Headlands with joints or faults | Progressive enlargement → collapse → isolated stack |
| Headlands & bays (discordant coast) | Erosion of soft rock, protection of hard rock | Alternating rock types perpendicular to shore | Hard‑rock protrusions (headlands) and eroded recesses (bays) |
| Beaches – dissipative vs. reflective | Deposition (balance of swash & backwash) | Energy & sediment supply dictate slope | Dissipative: fine sand, gentle slope, wide surf zone. Reflective: coarse pebbles, steep slope, narrow surf zone. |
| Spits & tombolos | Long‑shore drift & deposition | Low‑energy bays, estuaries, or sheltered inlets | Spit extends from coast; tombolo links island to mainland |
| Barrier islands & barrier beaches | Deposition within a sediment cell | Shelf with abundant sand, low gradient | Parallel ridges, lagoon behind, migrate landward with SLR |
| Dunes (fore‑ and hinter‑dunes) | Aeolian (wind) transport & deposition | Sand‑rich beach with on‑shore wind | Vegetation (e.g., marram grass) stabilises; important buffer |
| Salt‑marshes | Biogenic sediment trapping & accretion | Estuarine or sheltered low‑energy coasts | Vegetated, low‑lying; attenuates wave energy, provides habitat |
| Mangroves | Biogenic accretion, root‑matrix trapping | Tropical sheltered coasts, often behind a fringe of reefs | Complex root systems, high carbon sequestration, strong wave attenuation |
| Coral reefs (fringing, barrier, atoll) | Biogenic calcium‑carbonate accretion | Tropical, warm (23‑29 °C), clear, shallow water | Protect shorelines, high biodiversity, vulnerable to bleaching |
| Strategy | Advantages | Disadvantages | Effectiveness (hazard × scale) |
|---|---|---|---|
| Sea walls | Immediate, long‑term protection; predictable performance. | High construction & maintenance cost; can increase downdrift erosion; visual impact; limited against extreme surge + SLR. | Best on high‑energy, high‑value urban coasts (local scale). Less effective where sea‑level rise exceeds design height. |
| Groynes | Relatively cheap; widen beaches; boost local tourism. | Interrupt long‑shore drift → downdrift erosion; require periodic repair. | Effective on moderate‑energy, sediment‑rich coasts (site‑scale). Not suitable for large storm events. |
| Breakwaters | Protect harbours and extensive beach stretches; reduce wave energy over a wide area. | Can cause accretion on leeward side and erosion on windward side; may affect navigation. | Ideal for ports and low‑energy beaches (regional scale). Limited where deep‑water access is needed. |
| Beach nourishment | Preserves natural appearance; supports tourism & wildlife. | Requires repeated replenishment; source‑sand may be scarce; can disturb benthic habitats. | Works on low‑to‑moderate energy coasts with adequate sediment supply (site‑scale). Success depends on wave climate and sand compatibility. |
| Managed realignment | Creates space for natural processes; long‑term cost savings; enhances biodiversity and ecosystem services. | Social disruption; loss of land/value; political resistance. | Most viable on sparsely populated, low‑lying coasts with high erosion rates (regional scale). Requires strong governance and compensation schemes. |
| Living shorelines | Multiple ecosystem services (habitat, water‑quality improvement, carbon sequestration); aesthetically pleasing. | May be less effective against extreme storms; longer establishment period; limited to suitable substrate. | Ideal for low‑energy estuarine or lagoonal settings (site‑scale). Often used in combination with hard structures in high‑energy zones. |
Monetary valuation often fails to capture non‑market benefits such as cultural heritage, intrinsic biodiversity value and long‑term adaptive capacity. Discount rates can undervalue future benefits, and data gaps (e.g., precise sediment budgets, long‑term maintenance costs) introduce uncertainty into cost‑benefit calculations.
Location: Rhine–Meuse delta, southwestern Netherlands.
| Criterion | Positive outcomes | Limitations |
|---|---|---|
| Flood protection | Peak discharge reduced up to 30 %; lower long‑term dike‑raising costs. | Requires continuous monitoring; extreme events could still overtop new flood‑plains. |
| Environment | 30 km² of new wetland habitat; increased biodiversity and carbon sequestration. | Initial construction disturbance; succession trajectories uncertain. |
| Economic & social | Long‑term savings on dike maintenance; new recreation/tourism opportunities. | Compensation for relocated residents; opposition from some agricultural interests. |
| Scalability | Model adopted in other Dutch deltas and internationally (e.g., UK Thames Estuary). | High upfront land‑acquisition costs limit use on densely built‑up coasts. |
Create an account or Login to take a Quiz
Log in to suggest improvements to this note.
Your generous donation helps us continue providing free Cambridge IGCSE & A-Level resources, past papers, syllabus notes, revision questions, and high-quality online tutoring to students across Kenya.