18 Marine Heatwaves

18.1 Overview

Marine heatwaves (MHWs) are prolonged periods of anomalously warm ocean temperatures that can alter marine ecosystem structure and function. Defined formally by Hobday et al. (2016) as discrete warming events where sea surface temperatures exceed the local 90th percentile threshold for five or more consecutive days, MHWs have emerged as one of the most widely documented climate-related pressures on coastal and marine environments worldwide. Hobday et al. (2018) further introduced a categorisation scheme based on the magnitude of exceedance above the seasonal climatology, classifying events as Category I (Moderate), II (Strong), III (Severe), or IV (Extreme) — an intuitive, colour-coded scale analogous to the Saffir–Simpson hurricane classification. MHW frequency has increased by 34% globally since 1925, with average event duration increasing by 17% (Oliver et al., 2018), and projections indicate continued escalation through the 21st century.

The waters off Western Australia represent a globally recognised MHW hotspot, driven largely by the warm, poleward-flowing Leeuwin Current — the dominant boundary current in the southeast Indian Ocean. The strength of the Leeuwin Current varies interannually in response to El Nino–Southern Oscillation (ENSO) dynamics; during La Nina years, the current strengthens and delivers anomalously warm tropical water southward along the WA coast, creating conditions conducive to extreme warming events. The Leeuwin Current region has warmed at rates exceeding the global mean, with satellite records showing a long-term SST trend of approximately 0.01–0.02 \(^\circ\)C per year superimposed on high interannual variability. The most severe MHWs off WA tend to coincide with strong La Nina events, as occurred in 2011 and again in 2021–2022.

Cockburn Sound, as a semi-enclosed coastal embayment with restricted flushing and relatively shallow bathymetry, is exposed to the effects of MHWs. Elevated temperatures can compound existing pressures on the Sound’s marine ecosystems — depressing dissolved oxygen, promoting algal blooms, and directly stressing benthic communities including the seagrass meadows that form the ecological foundation of the Sound (Chapter 16; Chapter 17).

This chapter provides a general summary of marine heatwave conditions in the CSIEM domain. A satellite SST analysis undertaken using the heatwaveR detection framework.

18.2 MHW Event Detection

An interactive marine heatwave analysis has been developed for Cockburn Sound using the UKMO OSTIA satellite SST reanalysis product (1981–2025) and the heatwaveR detection framework (Schlegel & Smit, 2018). The analysis applies the Hobday et al. (2016) detection algorithm and the Hobday et al. (2018) categorisation scheme to the daily SST record (@ site 32.18\(^\circ\)S, 115.73\(^\circ\)E), located within Cockburn Sound.

The interactive report card includes a long-term SST time series with MHW events highlighted by category, an annual summary of MHW days, event intensity analysis and a MHE Evnt explorer.



18.3 The 2011 Marine Heatwave

The austral summer of 2010/2011 produced the most extreme marine heatwave recorded in Australian waters. A combination of a record-strength Leeuwin Current, a near-record La Nina event, and anomalously high air–sea heat flux into the ocean resulted in unprecedented warming along more than 2,000 km of the Western Australian coastline (Pearce et al., 2011; Pearce & Feng, 2013). Satellite-derived SST anomalies in February 2011 peaked at approximately +3 \(^\circ\)C above long-term monthly means over a broad area from Ningaloo (22\(^\circ\)S) to Cape Leeuwin (34\(^\circ\)S), extending more than 200 km offshore. Nearshore temperature loggers in the central west coast region recorded anomalies of up to +5 \(^\circ\)C above average over a period encompassing late February and early March (Pearce & Feng, 2013).

Rose, Smale and Botting (2012) provided the first detailed characterisation of the 2011 MHW within Cockburn Sound, using in-situ monitoring data from four long-term stations (CS4, CS9, CS11 in Cockburn Sound and WS4 in Warnbro Sound). A warming event of 2–4 \(^\circ\)C magnitude persisted for more than eight weeks from late January through April 2011. Bottom water temperatures at 10–20 m depth were statistically significantly higher than those recorded during the preceding nine years (2002–2010). Thermal Stress Anomalies (TSAs) — defined as weekly temperatures $$1 \(^\circ\)C above the warmest climatological week — were recorded at all monitoring sites, indicating sustained exceedance of maximum expected summertime conditions.

Dissolved oxygen levels were depressed at most monitoring sites during the event, being approximately 2 mg L\(^{-1}\) lower than the 2002–2010 mean in early March 2011. The combination of elevated temperatures (reducing oxygen solubility) and stimulation of biological oxygen demand likely contributed to this depression, with implications for hypoxic stress in the deeper basins of the Sound.

18.5 Ecological Responses

The ecological consequences of the 2011 MHW along the Western Australian coast were widespread. An estimated 43% of the kelp (Ecklonia radiata) along the west coast perished, and kelp habitat was replaced by turf algae, as mediated by feedback processes that have prevented kelp recovery more than a decade after the event (Wernberg, 2020). Hard corals at Rottnest Island also exhibited high rates of bleaching in May 2011, among the highest-latitude bleaching events recorded globally at that time (Thomson et al., 2011). Fish kills were reported at multiple locations, and temporary southward range extensions of tropical species including whale sharks and manta rays were observed (Pearce et al., 2011). Impacts on fishery stocks (Caputi et al., 2014), and changes in benthic community structure were also documented along the entire coast (Wernberg et al., 2012; Smale & Wernberg, 2012).

Within Cockburn Sound, ecological observations during the 2011 event included mortality of the sea star Archaster angulatus and algal bloom development. However, as noted in Rose et al. (2012), a paucity of historical ecological baseline data in the Sound has meant that uncertainity remains about the extent of biological responses of cumualtive heat stress. This underlies the importance of routine monitoring for thermally sensitive taxa to allow us to understan the ecological footprint of these events.

Research conducted under WAMSI’s Westport Marine Science Program (WWMSP) Theme 2 has advanced understanding of the thermal physiology of local seagrass species. Experimental work has established that Posidonia sinuosa — the dominant meadow-forming species in Cockburn Sound — exhibits declining net productivity at water temperatures above approximately 23–25 \(^\circ\)C, with sustained exposure to temperatures exceeding 27–28 \(^\circ\)C leading to tissue damage, reduced shoot density, and increased vulnerability to secondary stressors such as light limitation and epiphyte loading (WAMSI, 2024). These thermal thresholds are regularly exceeded during MHW events. The WWMSP program has also investigated the capacity of different Posidonia species and populations to acclimate to warming, finding that resilience varies among species and sites — information that is relevant to guiding restoration priorities and interpreting CSIEM model predictions of seagrass habitat suitability under future climate scenarios (Chapter 17).

Marine heatwaves act as compounding stressors on seagrass communities. Elevated temperatures directly reduce net photosynthesis and accelerate respiration in Posidonia sinuosa, narrowing the carbon balance and increasing the plant’s dependence on adequate light availability (Chapter 17). Simultaneously, warmer water promotes epiphyte and macroalgal growth, further reducing light at the leaf surface, while oxygen depression in bottom waters creates additional stress and promotes nutrient release (Chapter 12). Long-term trends in seagrass condition documented by Mohring and Rule (2013) indicate that Cockburn Sound meadows have experienced sustained pressure over the past two decades, and the recurrence of major MHW events in 2021–2022 and 2024–2025, following the 2011 event, suggests that recovery time between thermal stress episodes may be insufficient.

18.6 Summary

This chapter has provided an overview of marine heatwave conditions relevant to Cockburn Sound, drawing on satellite SST analysis, in-situ observations, and ecological research undertaken through the WAMSI Westport Marine Science Program. The MHW detection tool developed using the UKMO OSTIA reanalysis and the heatwaveR framework identifies three major events affecting Cockburn Sound since 2011, with the 2021–2022 event exceeding the 2011 benchmark in cumulative intensity. Ecological responses to these events in the broad region is thought to span kelp loss, coral bleaching, fishery impacts and seagrass stress, with Posidonia sinuosa observed thermal thresholds regularly exceeded during MHW periods. These observations inform the CSIEM model’s representation of heat-stress impacts on benthic habitats and water quality.


  • An MHW assessment for Cockburn Sound has been undertaken as part of the CSIEM platform, using satellite SST reanalysis and the heatwaveR detection framework
  • MHW frequency and cumulative intensity in the region appear to be increasing, with three major events since 2011 and shortening recovery intervals
  • Recent MHW events regularly produce temperatures in the 23–28 \(^\circ\)C range known to negatively impact Posidonia sinuosa productivity and survival