Fisheries and marine resource management (QCE Marine Science Unit 4)

What this dot point is asking

QCAA wants you to explain how fish populations are managed, define maximum sustainable yield, overfishing and bycatch, and evaluate real management strategies. "Evaluate" means weighing strengths against weaknesses, so you need to judge how well each strategy works, using Australian examples such as Great Barrier Reef zoning.

Key concepts

Maximum sustainable yield

A fish population grows fastest when it is at an intermediate size, because there is enough food and space for rapid breeding. The maximum sustainable yield (MSY) is the largest catch that can be taken year after year without reducing the population, by harvesting only the surplus the population produces. Fishing at MSY keeps the stock stable; fishing above it shrinks the stock.

Overfishing

Overfishing is harvesting faster than a population can replace itself, so the stock declines. If it continues, the population can collapse and may not recover even when fishing stops, because too few breeding adults remain. Slow-growing, late-maturing species (such as many sharks and the orange roughy fished in southern Australian waters, which lives for over a century) are especially vulnerable because they replace themselves slowly.

Bycatch

Bycatch is the non-target species caught and usually killed alongside the target catch, such as turtles, dugongs, dolphins and juvenile fish caught in trawl nets. Bycatch can drive declines in species that are not even being fished, which is why turtle excluder devices and bycatch reduction devices are required in Queensland prawn trawl fisheries.

Management strategies and their evaluation

• Catch quotas (total allowable catch). A legal cap on how much of a species can be taken each year, ideally set near MSY. Strength: directly limits harvest. Limitation: requires accurate stock data, which is costly and uncertain, and can encourage discarding of fish over the quota.
• Size and gear limits. Minimum size limits protect juveniles so they breed before capture; mesh-size and gear rules reduce bycatch. Strength: simple and enforceable. Limitation: undersized fish caught and released may still die.
• Seasonal and area closures. Closing spawning grounds during breeding (as Queensland does for some reef fish) lets stocks replenish. Strength: protects reproduction. Limitation: fishers may simply fish harder elsewhere or before the closure.
• Marine protected areas (MPAs) and no-take zones. Areas where fishing is banned act as refuges where populations rebuild and "spill over" to restock surrounding waters. The Great Barrier Reef Marine Park zoning plan (revised in 2004) increased no-take green zones from about 5 per cent to about 33 per cent of the park; coral trout populations inside green zones are now substantially larger than in fished zones, and the protected areas help re-seed fished areas with larvae. Strength: protects whole ecosystems, not just one species. Limitation: needs enforcement against poaching, and works only if zones are large and well placed.

Integrated management

Because impacts interact, the most effective approach combines strategies: quotas and gear rules to control harvest, protected areas to safeguard ecosystems, and catchment and climate action to address water quality and warming. Australia's combination of the Great Barrier Reef zoning plan, fishery quotas and the Reef Water Quality Improvement Plan is an example of this integrated approach, though its success ultimately depends on global action on emissions.

Why this matters

This dot point pulls together the whole subject: it applies the population and energy-flow ideas of Unit 3 and the impact and climate content of Unit 4 to the practical question of how to keep using the ocean without destroying it. Evaluating management strategies against evidence is exactly the skill assessed in the IA3 research investigation and the external exam.