3.2.2 Cyclones and wind

Cyclones are intense, large-scale, low-pressure weather systems that form over warm tropical waters and rotate, producing persistent destructive winds that can build extreme seas given sufficient time and fetch. The number of cyclones making landfall is not random over time.537 Rather, the frequency of landfall is higher during La Niña years than El Niño years 538,539 (Box 6.1). The number of cyclones has decreased across northern Australia since at least 1982, and likely since 1900 540 (Section 6.3.1). A continuing trend of decreasing cyclone numbers, but with an increasing average intensity, is expected along with typically large variations in cyclone numbers from year to year.540,541

Cyclones can disturb coastal and marine ecosystems through the high winds, waves, storm surge and heavy rain they generate, so they are important drivers of ecosystem change in the Region.179 Coral reefs, seagrass meadows, mainland and island beaches, and ecosystems on the coastal fringe, such as mangrove forests, are especially vulnerable to such impacts. For instance, mangroves can be damaged by high winds and inundation with salt water, and mangroves at the outer fringe can be wave damaged. 

Observed and projected global increases in the average severity of cyclones 542,543 (Section 6.3.1) have important implications for  Reef ecosystems (Section 6.3.2). For example, coral reefs can experience damage of widely differing severity, from breakage or removal of individual coral colonies to damage to the reef structure itself, depending on the intensity and duration of wave exposure.544 Cyclone-induced wave force and resulting damage varies at local scales due to factors like depth, the shape of the seafloor, the presence of physical barriers and reef orientation.545 Some species are more fragile than others and are more likely to break or dislodge under the force of the waves.544 In a healthy reef ecosystem, the patchiness of cyclone damage can promote diversity by creating a range of microhabitats and enabling the growth of corals with varying morphologies and rates of growth.546,547 Reef recovery depends on factors such as the severity and duration of exposure, the pattern and frequency of future disturbances,537 and the availability of suitable conditions for coral regrowth.548 If consolidated reef matrix is badly damaged recovery can be very slow.544

Post-cyclone reef scene with overturned plate coral, healthy soft corals, exposed coral debris and damselfish.
Overturned plate coral after cyclone Jasper at Fitzroy island. © Ryan Ramasamy 2024
Figure 3.3
Number and severity of cyclones, 1970–71 to 2023–24

Showing the number and category of cyclones that entered the Region between 1970–71 and 2023–24 (1 July–30 June). The cyclone category shown is the maximum category reached within the Region for a particular system. Cyclone categories have been determined based on the mean maximum windspeed recorded in the Region in kilometres per hour (kmph). Category 1: 63–88 kmph, Category 2: 89–117 kmph, Category 3: 118–159 kmph, Category 4: 160–199 kmph, Category 5: >200 kmph. This analysis method may exclude some cyclones which remained outside the Region but caused wave damage within the Region (such as cyclone Iris in 2017–18). Source: Commonwealth of Australia Bureau of Meteorology 558,559,560

Bar graph showing the number of cyclones to enter the Region through time. There were 17 years between 1970/71 and 2022/23, that did not experience any cyclones; 1976-77 experienced the most – four cyclones, ranging between category 2 and category 4.

The extent to which cyclone-induced waves damage coral reefs depends on a combination of the cyclone’s intensity, size and the length of time spent tracking near coral reefs.549 Although a trend of increasing intensity (but decreasing frequency) 540 appears to be emerging, future trends for the other determinants of damage to reefs (cyclone size and speed of travel) remain uncertain.549 Likewise, there is considerable uncertainty surrounding potential future shifts in locations and patterns of areas exposed to cyclones.549 While poleward shifts in the latitude of maximum intensity of cyclones have been observed in both northern and southern hemispheres,550 and there is evidence showing potential expansion of regions suitable for cyclones,551,552 it is unclear whether these trends are occurring in the Region.

Cyclones and other low-pressure systems can produce oceanic storm surges that cause serious damage to coastal infrastructure and ecosystems. One of the most certain future impacts from cyclones will be an increase in coastal flooding when storm surges are superimposed on higher sea levels (Section 3.2.5), increasing their destructive power.540,553 The probability of heavy rain events has also increased in recent decades due to regional warming (as warmer air carries more moisture), and it is projected to increase further as air temperatures continue to rise.540,554 Conversely, wave action associated with cyclones has been shown to upwell cooler water that can lower sea surface temperatures and reduce the impacts of coral bleaching at regional scales,555 while the cooling influence of increased cloud cover can also reduce sea surface temperatures at local scales.556

Cyclones remain key drivers of ecosystem change in the Region

Over the past 5 years, cyclone activity has been relatively low (Figure 3.3). Cyclone Trevor crossed the Region before making landfall on 23 March 2019 near the town of Lockhart River in Cape York as a category 3 system, causing significant damage on land. Impacts to the Reef were found to be minimal at long-term coral reef survey sites in the vicinity, noting most were well south of the cyclone’s track.557 Cyclone Kimi tracked through the Region in January 2021 reaching category 1 but not making landfall. Cyclone Tiffany reached category 2 intensity within the Region, before making landfall near Cape Melville on Cape York Peninsula on 10 January 2022 at category 1. Cyclone Jasper crossed the Reef before making landfall at Wujal Wujal, north of Cape Tribulation, on 13 December 2023 as a category 2 system. Cyclone Kirrily crossed through the Region in January 2024, making landfall at Townsville as a category 3 system. The period of relative quiescence before the successive cyclones in late 2023 and early 2024 saw a welcome recovery in coral cover (Sections 2.3.5, 2.4.4 and 8.3.1), highlighting that the Reef remains a resilient and dynamic ecosystem. Maintaining this resilience by addressing pressures amenable to management action is crucial for the long-term health of the Reef in the face of compounding impacts from climate change and ocean acidification.

Winds are an important influence on the Reef, affecting a range of processes, including the shaping of islands and coastlines, the movement and local characteristics of waves and currents, and distribution pathways of marine pollution.561 Established wind patterns can affect the breeding success and life history traits of reef animals such as corals, fish,562 and sea snakes.435 Any changes in wind patterns may affect connectivity within the Region, via the distribution of windborne seeds 563 and larvae of coral, fish and invertebrates.564 Climate change may affect wind speeds and patterns in the Region, but the specific changes are likely to be complex and are not yet well understood.565,566,567 

In the past 5 years, cyclone activity has been relatively low. However, large variation in the numbers of cyclones is expected, and cyclones remain one of the most important drivers of ecosystem change in the Region. A longer-term trend may be emerging of decreasing cyclone numbers and increasing average intensity.

References
  • 179. Lam, V.Y., Chaloupka, M., Thompson, A., Doropoulos, C. and Mumby, P.J. 2018, Acute drivers influence recent inshore Great Barrier Reef dynamics, Proceedings of the Royal Society B 285(1890): 20182063.
  • 435. Shine, R., Brown, G.P. and Goiran, C. 2022, Divergence in life-history traits among three adjoining populations of the sea snake Emydocephalus annulatus (Hydrophiinae, Elapidae), Scientific Reports 12(1): 5137.
  • 537. Wolff, N.H., Wong, A., Vitolo, R., Stolberg, K., Anthony, K.R., et al. 2016, Temporal clustering of tropical cyclones on the Great Barrier Reef and its ecological importance, Coral Reefs 35: 613-623.
  • 538. Ramsay, H.A., Camargo, S.J. and Kim, D. 2012, Cluster analysis of tropical cyclone tracks in the Southern Hemisphere, Climate Dynamics 39: 897-917.
  • 539. Lin, I., Camargo, S.J., Patricola, C.M., Boucharel, J., Chand, S., Klotzbach, P., Chan, J.C.L., Wang, B., Chang, P., Li, T. and Jin, F. 2020, ENSO and Tropical Cyclones, in El Niño Southern Oscillation in a Changing Climate, eds M.J. McPhaden, A. Santoso and W. Cai, American Geophysical Union, United States, pp. 377-408.
  • 540. CSIRO and The Bureau of Meteorology 2022, State of the Climate 2022.
  • 541. Cheal, A.J., MacNeil, M.A., Emslie, M.J. and Sweatman, H. 2017, The threat to coral reefs from more intense cyclones under climate change, Global Change Biology 23(4): 1511-1524.
  • 542. Wang, G., Wu, L., Mei, W. and Xie, S. 2022, Ocean currents show global intensification of weak tropical cyclones, Nature 611(7936): 496-500.
  • 543. Emanuel, K. 2021, Response of global tropical cyclone activity to increasing CO 2: Results from downscaling CMIP6 models, Journal of Climate 34(1): 57-70.
  • 544. Beeden, R., Maynard, J., Puotinen, M., Marshall, P., Dryden, J., et al. 2015, Impacts and recovery from severe Tropical Cyclone Yasi on the Great Barrier Reef, PloS One 10(4): e0121272.
  • 545. Massel, S.R. and Done, T.J. 1993, Effects of cyclone waves on massive coral assemblages on the Great Barrier Reef: meteorology, hydrodynamics and demography, Coral Reefs 12: 153-166.
  • 546. Harmelin-Vivien, M.L. 1994, The effects of storms and cyclones on coral reefs: a review, Journal of Coastal Research: 211-231.
  • 547. Halford, A., Cheal, A.J., Ryan, D. and Williams, D.M. 2004, Resilience to large‐scale disturbance in coral and fish assemblages on the Great Barrier Reef, Ecology 85(7): 1892-1905.
  • 548. Ceccarelli, D.M., McLeod, I.M., Boström-Einarsson, L., Bryan, S.E., Chartrand, K.M., et al. 2020, Substrate stabilisation and small structures in coral restoration: state of knowledge, and considerations for management and implementation, PLoS ONE 15(10): e0240846.
  • 549. Dixon, A.M., Puotinen, M., Ramsay, H.A. and Beger, M. 2022, Coral reef exposure to damaging tropical cyclone waves in a warming climate, Earth's Future 10(8): e2021EF002600.
  • 550. Kossin, J.P., Emanuel, K.A. and Vecchi, G.A. 2014, The poleward migration of the location of tropical cyclone maximum intensity, Nature 509: 349-352.
  • 551. Daloz, A.S. and Camargo, S.J. 2018, Is the poleward migration of tropical cyclone maximum intensity associated with a poleward migration of tropical cyclone genesis? Climate Dynamics 50(1-2): 705-715.
  • 552. Studholme, J., Fedorov, A.V., Gulev, S.K., Emanuel, K. and Hodges, K. 2022, Poleward expansion of tropical cyclone latitudes in warming climates, Nature Geoscience 15(1): 14-28.
  • 553. Knutson, T., Camargo, S.J., Chan, J.C.L., Emanuel, K., Ho, C., et al. 2020, Tropical cyclones and climate change assessment: part II: projected response to anthropogenic warming, Bulletin of the American Meteorological Society 101(3): E303-E322.
  • 554. Yaddanapudi, R., Mishra, A., Huang, W. and Chowdhary, H. 2022, Compound wind and precipitation extremes in global coastal regions under climate change, Geophysical Research Letters 49(15): e2022GL098974.
  • 555. Carrigan, A.D. and Puotinen, M. 2014, Tropical cyclone cooling combats region‐wide coral bleaching, Global Change Biology 20(5): 1604-1613.
  • 556. Leahy, S.M., Kingsford, M.J. and Steinberg, C.R. 2013, Do clouds save the Great Barrier Reef? Satellite imagery elucidates the cloud-SST relationship at the local scale, PLoS One 8(7): e70400.
  • 557. Australian Institute of Marine Science 2020, Princess Charlotte Sector 2020 Survey Report Summary, <https://www.aims.gov.au/reef-monitoring/princess-charlotte-sector-2020>.
  • 558. Bureau of Meteorology 2024, Tropical cyclone databases, <http://www.bom.gov.au/cyclone/tropical-cyclone-knowledge-centre/databases/>.
  • 560. Bureau of Meteorology 2024, Southern hemisphere tropical cyclone data portal, <http://www.bom.gov.au/cyclone/tropical-cyclone-knowledge-centre/history/tracks/>.
  • 561. Critchell, K., Grech, A., Schlaefer, J., Andutta, F.P., Lambrechts, J., et al. 2015, Modelling the fate of marine debris along a complex shoreline: Lessons from the Great Barrier Reef, Estuarine, Coastal and Shelf Science 167: 414-426.
  • 562. Russell, B.C., Anderson, G.R.V. and Talbot, F.H. 1977, Seasonality and recruitment of coral reef fishes, Marine and Freshwater Research 28(4): 521-528.
  • 563. Nathan, R., Schurr, F.M., Spiegel, O., Steinitz, O., Trakhtenbrot, A., et al. 2008, Mechanisms of long-distance seed dispersal, Trends in Ecology & Evolution 23(11): 638-647.
  • 564. Cowen, R.K. 2002, Larval dispersal and retention and consequences for population connectivity in Coral reef fishes: dynamics and diversity in a complex ecosystem, ed. P.F. Sale, Academic press, pp. 149–170.
  • 565. Moise, A., Abbs, D., Bhend, J., Chiew, F., Church, J., et al. 2015, Monsoonal north cluster report. Climate change in Australia projections for Australia's natural resource management regions, CSIRO and Bureau of Meteorology, Australia.
  • 566. Dowdy, A., Abbs, D., Bhend, J., Chiew, F., Church, J., et al. 2015, East coast cluster report. Climate change in Australia projections for Australia's natural resource management regions, CSIRO and Bureau of Meteorology, Australia.
  • 567. Greene, S., Morrissey, M. and Johnson, S.E. 2010, Wind climatology, climate change, and wind energy, Geography Compass 4(11): 1592-1605.