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IB Syllabus Requirements for Ocean management futures
B.4.1
Growing demand for abiotic ocean resources
B.4.2
Biotic resources and alternatives to overfishing
B.4.3
Managing ocean pollution
B.4.4
Strategic oceans and geopolitical conflict
B.4.1
GROWING DEMAND FOR ABIOTIC OCEAN RESOURCES
Abiotic resources come from the non-living environment. In the ocean, these include oil and natural gas beneath the seabed, sand and gravel used in construction, and metal-bearing seabed deposits.
As populations grow, industrialization spreads and consumption rises, demand for energy and raw materials increases. Oil supports transport and petrochemical production. Natural gas supplies heating, electricity and industry, while demand for batteries, electrical infrastructure and other technologies encourages interest in metals such as nickel, cobalt and copper.
Demand doesn't rise evenly everywhere, nor does it rise indefinitely. Energy transitions and recycling alter the amount and type of resources required, as do prices and economic conditions. Even so, depletion of accessible land-based deposits can make offshore resources more attractive.
With improved seismic surveying, drilling and remotely operated equipment, companies can explore deeper water and more difficult environments. Extraction becomes commercially attractive when expected revenue exceeds the costs of exploration, operation and transport. High demand alone doesn't guarantee a profitable deposit.
Extraction can create jobs and generate export earnings and government revenue, while providing a more secure energy supply. Ports and associated industries may grow. However, specialist employment and profits can flow elsewhere rather than stay in nearby coastal communities.
Drilling and mining can disturb habitats. They can also generate noise and introduce pollutants, while oil spills may damage fisheries and tourism far beyond the extraction site. Seabed mining removes or damages habitats and creates sediment plumes. Because deep-sea ecosystems remain uncertain, their recovery is difficult to predict. Commercial exploitation of deep-sea minerals is still much less established than offshore oil and gas production.
Burning extracted oil and gas also releases greenhouse gases. The consequences of resource use therefore reach across several scales: seabed disturbance is local, whereas pollution may spread regionally and emissions affect the global atmosphere. Competition for valuable deposits can intensify disputes over maritime boundaries.
B.4.2
BIOTIC RESOURCES AND ALTERNATIVES TO OVERFISHING
Biotic resources come from living organisms. Ocean fisheries provide food and employment, as well as products for trade. Marine mammals have been exploited for meat, oil and other materials.
Demand for fish worldwide has risen as populations and incomes have grown and international trade has expanded. Wild capture production has broadly levelled off instead of keeping pace; aquaculture, by contrast, has expanded strongly. The global pattern hides major differences between stocks. Some have recovered under management. Others remain depleted or face excessive fishing pressure.
Overfishing occurs when fishing removes fish faster than a stock can replenish itself over time. With larger vessels, improved fish-finding technology and refrigeration, fleets can exploit more distant waters. Subsidies and weak enforcement can keep fishing pressure high even as stocks decline.
Commercial exploitation greatly reduced many whale populations. International restrictions have reduced commercial whaling, allowing some populations to recover, though recovery remains uneven. Hunting continues under different national policies and arrangements, including some Indigenous subsistence hunting. Even where deliberate hunting is restricted, marine mammals face threats from bycatch—the unintended capture of non-target organisms.
Aquaculture is the farming of aquatic organisms. It can supply more food without directly increasing wild capture. Its effects, however, depend on which species are farmed and how they are produced.
| Approach | Potential benefits | Limitations affecting viability |
|---|---|---|
| Aquaculture | Provides a more controllable supply and employment; farming shellfish and seaweed can require little or no feed from wild fish. | Some farmed fish need wild-caught feed; waste and disease, along with escapes and coastal habitat loss, can create new pressures. |
| Marine conservation areas | Protect habitats and breeding populations; effective no-take zones may help stocks recover and spill over into surrounding fisheries. | Results depend on location and size, as well as connectivity and enforcement; fishing pressure may move elsewhere. |
| Catch quotas | Limit removals and can help stocks recover when based on reliable assessments. | Uncertain stock estimates and illegal fishing can undermine limits, as can misreporting and poorly designed rules. |
Restrictions vary between conservation areas: designation doesn't automatically prohibit all fishing. A quota, too, protects a stock only if the limit is biologically appropriate and catches are monitored.
No single alternative solves every problem. Protected breeding areas can work alongside quotas and selective fishing equipment, while appropriately managed aquaculture supplies part of the demand. Recovery may reduce incomes at first. Cooperation and support for fishing communities therefore affect whether restrictions remain workable.
Judge success by stock condition and ecosystem health, as well as production. A larger harvest is not evidence of sustainability if it comes from a shrinking breeding population.
B.4.3
MANAGING OCEAN POLLUTION
Ocean pollution is hard to manage. Sources occur both on land and at sea, and currents carry pollutants across administrative boundaries. Preventing pollution usually brings greater long-term benefits than trying to recover material once it has dispersed.
Local measures target identifiable sources and damaged places; global agreements set shared rules for shipping, dumping and cross-border waste movements. Both are needed. International rules achieve little unless they are implemented, and local action cannot control every external source.
Accidents, historical dumping or authorized liquid discharges may cause radioactive contamination. The risk depends on the radionuclide and its concentration, as well as exposure pathways and persistence. Radioactive materials should not be treated as though they all have identical effects.
Locally, contaminated water can be contained and discharges treated. Strategies also include monitoring water and seafood, with harvesting restricted where necessary. These measures can reduce exposure. Treatment, however, produces wastes that need secure storage, and some contaminants are difficult or costly to remove.
The London Convention and Protocol restrict disposal of radioactive waste through international controls on sea dumping. Regional cooperation, such as OSPAR in the north-east Atlantic, addresses radioactive discharges and monitoring. Shared standards and coordinated evidence are strengths of these approaches. They depend on national compliance, though, and historical contamination persists. Controls on dumping do not automatically eliminate every land-based discharge.
Equipment maintenance and inspection help prevent oil pollution locally, alongside emergency planning. After a spill, booms and skimmers may contain and recover surface oil. Shoreline cleaning reduces some coastal impacts, but recovery is limited by rough seas and rapid spreading, as well as inaccessible coastlines. Dispersants can reduce surface slicks; the trade-off is increased exposure within the water column.
At the global level, MARPOL sets rules to reduce pollution from ships, including controls on oil discharges. Vessel design requirements and port inspections, together with liability arrangements, strengthen prevention and encourage responsible operation. Enforcement varies. Shipping agreements also leave some sources of oil pollution uncovered, such as some offshore extraction accidents.
Local strategies reduce unnecessary packaging and improve waste collection. They also intercept litter in rivers and drains and provide facilities for discarded fishing gear. Beach clean-ups remove visible waste and can protect wildlife. They don't stop continuing inputs, however, or recover most dispersed microplastics.
MARPOL Annex V prohibits disposal of plastics from ships. Cooperation between countries on waste shipments can also reduce inappropriate transfers to places with insufficient management capacity. These approaches address important pathways. Much marine plastic originates on land, though, so shipping rules alone cannot solve the problem.
| Management approach | Main strength | Main weakness |
|---|---|---|
| Source reduction and prevention | Prevents pollution from spreading and usually reduces future clean-up costs. | Requires changes in production and infrastructure, as well as behaviour. |
| Local containment and clean-up | Allows a quick response to a particular incident or contaminated site. | Recovery is incomplete, and pollutants may already have moved elsewhere. |
| International regulation | Coordinates action across borders and sets common obligations. | Depends on coverage and monitoring, as well as finance and enforcement. |
A fall in pollution at one monitored beach does not necessarily show an ocean-wide improvement. Assessment must account for continuing inputs and movement between places, along with ecological effects and the time needed for recovery.
B.4.4
STRATEGIC OCEANS AND GEOPOLITICAL CONFLICT
Oceans link producers to markets. They also hold valuable resources and provide routes for naval movement, so states seek secure access to sea routes and influence over strategically important locations.
Sovereignty is a state's authority over its territory. At sea, it differs from the more limited rights a state holds over resources. An exclusive economic zone normally extends up to 200 nautical miles from coastal baselines and gives a coastal state rights over resources—not complete ownership of the water or unrestricted control over navigation.
The oceans are often described as a global commons: a shared domain beyond exclusive national ownership. Yet ocean space does not all have the same legal status. Different rules apply to territorial seas, exclusive economic zones and areas beyond national jurisdiction.
Islands can support military facilities and influence maritime claims. Disputes may concern sovereignty or the maritime rights an island generates; overlapping claims to surrounding waters can also cause conflict. Not every feature generates the same maritime entitlements.
Canals shorten journeys between ocean basins. If a canal closes, access is restricted or traffic is disrupted, journeys can become longer, shipping costs can rise and deliveries can take more time. Control of a canal also brings revenue and political leverage, though both users and controlling states have an interest in keeping traffic moving.
A transit choke point is a narrow passage through which substantial maritime traffic must pass. When shipping is concentrated in this way, it is vulnerable to accidents and piracy, as well as military threats and obstruction. Disruption can reach far beyond the passage itself, affecting distant economies that depend on energy or traded goods.
The class chooses its own contemporary contested ocean area. To develop the case study, locate the dispute and identify the actors and their competing claims. Explain the area's strategic and resource value, then trace the consequences and attempts to manage the dispute.
Surveying and drilling activities have increased tensions, with naval deployments accompanying them at times. Competing maritime agreements and negotiations show how legal claims operate alongside diplomacy and power. The consequences include uncertainty for energy investment. Security risks and pressure on regional relationships are also part of the picture.
Gas alone does not explain the dispute. Island geography and the divided status of Cyprus also shape it, along with differing interpretations of maritime rights and wider alliances. Because this is a contemporary case, the class's chosen account should include a dated recent development rather than treat the situation as fixed.
B.4.5
SPATIAL INTERACTIONS ACROSS OCEANS AND COASTS
Spatial interactions are connections through which a change in one place affects another. In oceans, currents and organism movements provide these links, as do trade, investment and political decisions.
Currents and winds may carry pollution released near one coast towards another. Distance from the source alone doesn't determine exposure: the transport pathway matters too. A nearby sheltered coast may receive less pollution than a more distant one lying directly along its route.
Protecting a breeding habitat may benefit fishing grounds elsewhere as larvae disperse or adult fish move beyond the protected area. Heavy exploitation of a migratory stock in one jurisdiction, by contrast, can reduce catches in another.
Management can shift pressure elsewhere. Closing one fishing ground may push vessels into neighbouring waters; restricting extraction in one place may encourage investment elsewhere. Conditions can improve locally while deteriorating somewhere else.
The outcomes are unequal. A place that gains revenue from exploitation may not bear the pollution costs. To be effective, management must follow the relevant flows and connections rather than stop at an administrative boundary.
B.4.6
SCALES OF EXPLOITATION AND MANAGEMENT
Ocean exploitation ranges from small coastal fisheries to multinational fleets and energy companies. Management has to address where an activity takes place as well as the wider system that supports it.
| Scale | Typical responsibilities | Main constraint |
|---|---|---|
| Local | Communities set fishing rules, collect waste, protect habitats and respond to incidents. | Finance is limited, as is authority over external sources or visiting fleets. |
| National | Governments license activities, set quotas, plan coastal use and enforce rules within national jurisdiction. | Stocks, pollutants and commercial networks cross borders. |
| Regional | States cooperate over shared seas, migratory stocks and transboundary pollution. | Their priorities, capacities and interests may differ. |
| Global | Shared shipping rules and frameworks cover areas beyond national jurisdiction. | Agreements depend on states participating and implementing them. |
A locally managed conservation area may need national legal recognition. It may also depend on regional cooperation over migrating fish and international action against illegal fishing. Local plastic collection works better when national systems reduce waste leakage, alongside international rules that address shipping and waste transfers.
A scale mismatch occurs when the reach of a problem differs from the reach of the institution managing it. A municipality cannot control pollution arriving from another country's river. Nor can one state independently secure a stock harvested across several jurisdictions.
Managing at a larger scale isn't automatically better. Global rules offer broad coverage, while local institutions may understand livelihoods and conditions more closely. Effective arrangements combine shared objectives with responsibilities, resources and enforcement at the scales where action is needed.
B.4.7
PERSPECTIVES ON OCEAN MANAGEMENT
Groups judge ocean management according to their own interests. A measure may improve the ecosystem yet bring immediate costs for people who depend on access to a resource.
A no-take area, for example, may protect breeding fish while taking away a nearby fishing ground. Healthier marine habitats may appeal to tourism businesses. Fishers, meanwhile, may have to travel further and lose income. Stock recovery may bring wider benefits over time, but households won't necessarily see those benefits immediately—or at all.
| Perspective | Possible priority | Possible concern |
|---|---|---|
| Coastal fishing communities | Reliable livelihoods and continued access. | Restrictions imposed without participation or support. |
| Governments | Revenue, employment, food security and strategic interests. | Enforcement costs and conflict with other policy goals. |
| Extraction and shipping companies | Predictable rules and commercially viable operations. | Compliance costs, delays and liability. |
| Conservation organizations | Biodiversity, habitat recovery and reduced pollution. | Weak protection, exemptions and inadequate monitoring. |
| Indigenous communities | Cultural relationships with marine resources and decision-making rights. | Loss of customary access or exclusion from management. |
These priorities aren't fixed positions. People within a group may disagree, and different groups may share interests.
To judge effectiveness, first ask which objective is being assessed. Increasing the area of protected ocean counts as an administrative achievement. Ecological success, though, requires evidence that habitats or populations are healthier. Sustained incomes might indicate economic success; fair access and meaningful participation might indicate social success.
An assessment should separate short-term costs from long-term benefits, then identify who receives each. It should examine enforcement and whether exploitation has been unintentionally displaced elsewhere. Uncertainty matters too, as does what would probably have happened without the measure.
A balanced judgment explains the outcomes and how they are distributed. Management is more likely to last when it delivers measurable environmental improvements and those affected regard it as legitimate.
B.4.8
REPRESENTING OCEAN–ATMOSPHERE INTERACTIONS
Choose a graphic that makes a particular relationship visible. Maps reveal spatial patterns; time-series graphs show change. Annotated diagrams explain processes. Whichever you use, you still need to identify what the variables, arrows and symbols mean.
On a current map, arrows show flow direction. Wind arrows show the atmospheric influence. The legend must explain whether arrow length represents speed or is merely schematic. Adding routes and coastal locations can connect physical movement with pollution exposure or resource use.
Use a line graph to show how sea-surface temperature, wind conditions or pollution measurements change over time. When comparing different variables, make their units and scales clear. A scatter graph can show whether two measured variables vary together. That association alone, though, does not establish causation.
In a systems diagram, distinguish stores or components from transfers. Label arrows with the process—such as evaporation, heat transfer or wind stress—instead of leaving the connections unexplained. To show a feedback, include a complete loop and explain how it reinforces or reduces the initial change.
Separate measured information from conceptual illustration. A schematic explains a possible pathway, but it does not establish its magnitude. A measured graph provides evidence only for the locations and period it states.
How you represent information affects how readers interpret it. Map scale can hide local differences. Averages can conceal seasonal variation, while axis choices can exaggerate or compress change. Clear titles and dates, together with units, legends and source information, allow ocean–atmosphere graphics to support reliable explanations.