Weekend soft-sediment field exercise (Tupira Point & Pilot Bay)
For students driving to Pilot Bay: meet 12:00 noon sharp at Pilot Bay Boat Ramp (time moved 1 h later after re-checking tides).
For students nearer Tupira Point: arrive 11:00 AM to start as tide drops.
Footwear & clothing
You will be standing ankle–mid-calf in water; feet inevitably wet.
Options: gumboots (can flood), wetsuit boots, sports shorts, roll-up trousers, quick-dry fabrics.
Bring spare clothes; bus has ample storage.
Resources to print & bring
Fieldwork protocol + soft-sediment ID guides posted on Moodle.
Coral reef ecology, especially reef-building corals (hermatypic Scleractinians).
Reef structure, biodiversity, interspecific interactions.
Current threats (bleaching, predators, climate, run-off) & recovery dynamics.
Role of Marine Protected Areas (MPAs) as a positive case study.
Reef builders restricted to tropical 20 ° isotherm band: \approx\,23–29^\circ\,\text{C} surface water.
Found in oligotrophic, sunlit, shallow (< 30 m) zones of Indian & Pacific Oceans.
Coral Triangle (Malaysia → Indonesia → PNG → Solomon Is. → Philippines):
> 600 of \ge 800 known reef-building species occur here.
Nicknamed “marine Amazon” – extreme biodiversity within nutrient-poor ‘desert’ seas.
Volcanic island emergent → cooling & subsidence produces:
Fringing reef: coral attached to shore.
Barrier reef: lagoon separates reef from sinking island.
Atoll: island fully submerged; reef ring surrounds shallow lagoon; lagoon infilled by biogenic sand.
Cross-section zonation
Fore-reef (seaward slope): high-energy waves; massive, robust corals (e.g. brain coral).
Reef crest: greatest wave impact; high recruitment.
Back-reef & lagoon: sheltered; branching, delicate forms; patch reefs.
All key taxa (corals + coralline algae) precipitate CaCO₃ (calcite or aragonite) skeletons.
Reef accretion both upward (toward light) & seaward.
Growth relatively slow → vulnerable to sea-level rise out-pacing accretion.
Hermatypic (reef builders): Order Scleractinia; rigid stony skeleton.
Ahermatypic (soft corals): lack massive skeleton; solitary or colonial; present on reefs but do not build framework.
Polyp = mini-anemone inside skeletal cup.
Zooxanthellae (symbiotic dinoflagellate algae) reside in gastrodermis.
Mutualistic nutrient loop
Coral respiration provides \text{CO}2 + \text{H}2\text{O} → captured for photosynthesis.
Photosynthate (glucose, glycerol, amino acids) → \approx 90\% translocated to host; fuels tissue growth & CaCO₃ deposition.
Algae gain protection, stable light habitat, metabolic waste nutrients.
Explains paradox of high productivity (up to 5000\ \text{g C m}^{-2}\text{ yr}^{-1}) in nutrient-poor water.
Asexual: budding → clonal colony growth.
Sexual: mass synchronous broadcast spawning (usually night; lunar-timed).
Reliant on precise environmental cues: seasonal temperature trend, photoperiod, lunar phase.
Ensures gamete encounter in sessile organisms, facilitates long-distance larval dispersal.
Light: must remain in photic zone (< 30 m, turbidity-dependent).
Temperature: 23–29^\circ\,\text{C} typical, some Red Sea strains tolerate \ge 34^\circ\,\text{C}.
Salinity: 32–40 ‰.
Moderate water movement (gas exchange, nutrient delivery, larval supply).
Intolerance to:
Prolonged emersion during low tides.
High sedimentation (clogs polyps + reduces light).
Rapid sea-level rise, ocean warming, acidification.
Limited suitable substrate → intense interspecific & intraspecific competition.
Defensive/offensive mechanisms
Digestive filaments: corals extrude mesenterial filaments to digest neighbour tissue.
Sweeper tentacles: long nematocyst-laden extensions harpoon rivals.
Mucus toxins, over-topping growth, allelopathic chemicals.
Long-term outcome: patch mosaics; evolutionary trade-off between aggression & growth form.
Fish diversity far exceeds structural expectation; examples per reef region:
GBR (~1625 spp), Fiji (~1000 spp), Philippines (~1900 spp).
Herbivores (parrotfish, surgeonfish) “lawn-mow” fleshy algae → prevent algal overgrowth.
Predators (wrasses, triggerfish) control invertebrate coral eaters.
Loss of key functional groups destabilises coral–algae balance.
Voracious coral predator; episodic population explosions → whole-reef devastation.
Drivers of outbreaks
Removal of natural predators (bumphead wrasse, triton snail, lobsters) via overfishing/collecting.
Enhanced larval survival from nutrient run-off + warmer water.
Management tools
Diver injection programs (must avoid stabbing; induces spawning).
eDNA surveillance for early detection; ROVs with AI recognition + toxin injection.
El Niño lowered sea level, raised SST by \sim2–3^\circ\,\text{C}, increased storminess.
Up to 90 % coral mortality; subsequent urchin boom delayed recovery (decades).
Heat stress → expulsion of zooxanthellae → white skeleton visible.
Analogy: heat waves act like “underwater forest fires.”
Filmed in documentary Chasing Coral; current events on Ningaloo Reef (news 2023/24).
Late 1980s: overfishing removed ~80\% of reef fish biomass.
Hurricanes + coral diseases + nutrient influx.
Coral cover dropped from \sim52\% → \sim5\%; algae now ~90\% cover.
Represents shift to new stable algal-dominated state; recruitment window for corals closed.
Stressors operate at different scales:
Global: warming, acidification, cyclone frequency.
Local: overfishing, sediment, nutrient run-off.
Layering pushes reefs past resilience threshold → irreversible phase shift.
Red Sea Porites drill-core analysis
Chronology back to 1920; stress bands (dark CT bands) mark disturbance years.
2015: universal stress bands despite not being hottest year.
Massive nitrogen run-off combined with elevated SST (sub-threshold) produced bleaching.
Key takeaway: local water-quality management can mitigate global heat stress impacts.
Five criteria for effective MPA (Edgar et al. 2014):
No-take fishing ban.
Enforcement effective (not paper parks).
> 10 yrs old (ecological maturation).
> 100 km² size.
Isolation from direct land influence.
Outcomes compared to fished sites:
Target fish biomass ↑ dramatically, followed by non-target species.
Crown-of-thorns outbreaks ↓ frequency.
Coral cover % significantly higher within reserves.
GBR zoning plan (AIMS) – exemplar but faces sociopolitical challenges from fisheries sector.
Reefs supply food security (fishery nursery grounds), shoreline protection, tourism revenue, pharmaceutical bio-prospects.
Loss undermines economies of many tropical nations; cultural heritage at risk.
Management must blend climate action (mitigation), watershed practices (run-off control), and ecosystem-based fisheries regulations.
Thermal tolerance: 23–29^\circ\,\text{C}\;(common); stress threshold \approx32^\circ\,\text{C} (Red Sea case).
Salinity requirement: 32–40\ \text{‰}.
Primary productivity peak: \le 5000\;\text{g C m}^{-2}\text{ yr}^{-1}.
Coral Triangle species count: >600/800 spp.
Explain Darwin’s fringing → barrier → atoll succession.
Compare hermatypic vs ahermatypic corals (skeleton, symbiosis, habitat role).
Diagram coral polyp + zooxanthellae nutrient cycling.
Discuss Goldilocks constraints (light, T°, salinity, turbidity) and how climate change alters each.
Outline mechanisms and ecological consequences of coral bleaching.
Evaluate effectiveness & limitations of COTS management options.
Trace Jamaican reef phase shift as a case study of compounded stressors.
Interpret stress-band core data: what environmental reconstructions are possible?
List 5 attributes of successful MPAs and relate them to GBR outcomes.
Barnes & Hughes “An Introduction to Marine Ecology” – Coral chapters.
Nybakken & Bertness “Marine Biology: An Ecological Approach.”
Primary papers cited in lecture (full bibliography on final slide of original PPT).