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Anemonefish facilitate bleaching recovery in a host sea anemone


Ocean warming is causing the symbioses between cnidarians and their algal symbionts to breakdown more frequently, resulting in bleaching. For sea anemones, nutritional benefits derived from hosting anemonefishes increase their algal symbiont density. The sea anemone-anemonefish relationship could, therefore, facilitate bleaching recovery. To test this, bleached and unbleached sea anemones, both with and without anemonefish, were monitored in the laboratory. At the start of our experiment, algal symbiont density and colour score were lower in the bleached than unbleached sea anemones, whereas total chlorophyll remained similar. After 106 days, bleached sea anemones with anemonefish had an algal symbiont density and colour score equal to the controls (unbleached sea anemones and without anemonefish), indicating recovery had occurred. Furthermore, total chlorophyll was 66% higher in the bleached sea anemones with anemonefish than the controls. In contrast, recovery did not occur for the bleached sea anemones without anemonefish as they had 78% fewer algal symbionts than the controls, and colour score remained lower. Unbleached sea anemones with anemonefish also showed positive changes in algal symbiont density and total chlorophyll, which increased by 103% and 264%, respectively. Consequently, anemonefishes give their host sea anemones a distinct ecological advantage by enhancing resilience to bleaching, highlighting the benefits of symbioses in a changing climate.


Symbioses, where dissimilar organisms have evolved to coexist, are essential for maintaining ecosystem functions1,2,3. These associations can alleviate climate change impacts4,5,6. For instance, the relationship between endophytes and rice reduces host water requirements and facilitates drought tolerance7; and coral reef Trapeziid crabs clean sediments from habitat-providing corals, supporting host survival and growth8. Anthropogenically induced stressors of natural ecosystems are increasing globally, and furthering our knowledge of symbioses may offer new insights into mechanisms that enhance organisms' resilience to threats such as climate change9.

The symbioses between habitat-forming cnidarians, such as corals and sea anemones, and unicellular algae of the family Symbiodiniaceae provide a major source of primary production in many marine systems10. These algae are located within the cnidarians' gastrodermal tissue, where they photosynthesise producing sugars that support host growth and reproduction, and positively influence host fitness11,12,13. Here, the endosymbionts gain access to in hospite nutrients, such as ammonium, improving their condition and density13,14,15,16,17. However, during times of environmental stress, this relationship can breakdown, with the loss of Symbiodiniaceae and or their photosynthetic pigment (chlorophyll) causing the host to lighten and become ‘bleached’18. Bleaching reduces the photosynthates available to the host, and if the cnidarian remains bleached for a prolonged period, starvation can result in mortality19,20. Consequent ecosystem-wide changes can occur, such as decreased coral and sea anemone cover21,22,23, algal dominated phase shifts24,25,26 and long-term decreases in fish abundance and biodiversity27,28,29.

All ten sea anemone species that provide habitat for obligate symbiotic anemonefishes are susceptible to bleaching30. Bleaching has been documented in numerous tropical and subtropical locations throughout their Indo-Pacific distribution and can result in sea anemone mortality31,32,33,34. Subsequent reductions in anemonefish abundance occur as anemonefishes cannot survive in the field without their host sea anemones31,32,33,34. Depending on the severity, sublethal impacts can occur to the sea anemones, such as oxidative stress and decreased size33, 35. Bleached sea anemone habitat has cascading consequences for anemonefishes, including decreased fecundity, increased metabolic demand, increased stress hormones, and vulnerability to predators due to behavioural changes36,37,38.

Anemonefishes provide numerous benefits to their host sea anemones, including excreting metabolic waste in the form of ammonia17. Ammonia bonds to hydrogen ions in seawater, becoming ammonium. As a result of the anemonefishes' close physical proximity to their host sea anemone, the ammonium assimilates in the sea anemone cytoplasm via inward diffusion14,15. Symbiodiniaceae then absorb ammonium via reverse translocation39. Through this nutritional pathway, anemonefish presence increases endosymbiont density17. As Symbiodiniaceae density increase, so too do the photosynthates available to the sea anemone, and therefore when sea anemones are occupied by anemonefish, they have higher growth, asexual reproduction, tentacle expansion, and survival40,41,42.

Given the nutritional benefits of hosting anemonefishes, we aimed to determine if anemonefish can facilitate Symbiodiniaceae recovery in a host sea anemone following thermal bleaching. Entacmaea quadricolor, the bulb-tentacle sea anemone, was used as it is geographically widespread, relatively abundant, and provides habitat for 13 anemonefish species43. Furthermore, E. quadricolor is vulnerable to ocean warming, having a bleaching threshold of ~ 1 °C above the current summer maximum in subtropical eastern Australia44. Bleached and unbleached sea anemones were assigned to the following treatments: with an adult anemonefish pair (Amphiprion akindynos); without anemonefish (control) and; without anemonefish but with inaccessible fish food pellets added to the aquaria (procedural control). Recovery was deemed to have occurred when the response variables in the bleached sea anemones were statistically similar to the unbleached controls. We hypothesised that: (i) bleached sea anemones with anemonefish would recover, with no significant difference in Symbiodiniaceae density, total chlorophyll, or colour score in comparison to unbleached control sea anemones; (ii) bleached sea anemones without anemonefish would be unable to recover during the experimental timeframe; and (iii) unbleached sea anemones with anemonefish would have increased Symbiodiniaceae density and total chlorophyll due to the nutritional benefits received.


Symbiodiniaceae density

At the start of the experiment, there was a clear difference in Symbiodiniaceae density per mg of host protein between the bleached and unbleached sea anemones (Fig. 1a). As time progressed, little change was seen in the bleached and unbleached controls (the bleached procedural control and control are herein pooled, as are the unbleached procedural control, for all tests due to no statistical differences, n = 16 for both, see Supplementary Table 1). However, Symbiodiniaceae densities increased substantially from day 77 in both the bleached and unbleached sea anemones that hosted anemonefish (n = 8 per treatment). After 106 days, Symbiodiniaceae density had fully recovered in the bleached sea anemones with anemonefish, with no significant difference found when tested against the unbleached controls (P = 0.877). In contrast, the bleached controls did not recover: these contained 78% fewer algal symbionts than in the unbleached controls (P = 0.002). Unbleached sea anemones that hosted anemonefish had the highest Symbiodiniaceae density compared to other experimental treatments, increasing 103% over the 106 days (unbleached with anemonefish v bleached with anemonefish, P = 0.021; unbleached with anemonefish v unbleached controls, P < 0.001).

Figure 1
figure 1

(a) Symbiodiniaceae density per mg of host protein, (b) total chlorophyll per mg of host protein and (c) colour score throughout the experiment (mean ± SE, n = 8). Note the control and procedural control treatments are shown on these graphs. However, these were pooled for statistical analyses and described as such in the supporting text.

Total chlorophyll

Total chlorophyll per mg of host protein was similar among all treatments on day 0 (Fig. 1b). Over time, little change was observed in the bleached controls; whereas an increase was seen in all other treatments, with the greatest rate of change occurring in the sea anemones that hosted anemonefish. Both the bleached and unbleached sea anemones with anemonefish had significantly higher chlorophyll than the unbleached controls at the end of the experiment (66% higher, P = 0.005; 117% higher, P < 0.001, respectively). In contrast, total chlorophyll in the unbleached and bleached sea anemones without anemonefish did not differ at the end of the experiment (P = 0.125), and no differences were found between the unbleached and bleached sea anemones with anemonefish (P = 0.106).

Colour score

Over time, colour score increased only in the sea anemones that hosted anemonefish (Figs. 1c, 2). The colour score of bleached sea anemones with anemonefish was not significantly different from the unbleached controls by day 106 (P = 0.609), indicating recovery. In contrast, the colour score was 46% lower in the bleached controls than unbleached controls (P < 0.001), signifying recovery had not occurred. Overall, the unbleached sea anemones with anemonefish had the highest colour score (unbleached with anemonefish versus bleached with anemonefish, P = 0.033; unbleached with anemonefish versus unbleached controls, P = 0.004).

Figure 2
figure 2

Sea anemones indicative of each treatment at the beginning (day 0) and end (day 106) of the experiment. The E hue colour score from the CoralWatch Coral Health Chart was used to assess visual changes.


All sea anemones survived, except for one bleached control, and a small fragment (resulting from fission) from one bleached sea anemone with anemonefish. Fission occurred in bleached sea anemones with anemonefish, with a mean of 0.75 ± SE 0.37 clonal descendants per sea anemone by the end of the experiment. For the unbleached sea anemones with anemonefish, there were 0.38 ± 0.26 mean clonal descendants per sea anemone. In contrast, in the bleached sea anemones without anemonefish treatment, there were only 0.06 ± 0.06 mean clonal descendants per sea anemone. Fission did not occur in any of the unbleached sea anemones without anemonefish.


Anemonefish facilitated bleaching recovery in a host sea anemone, thereby enhancing resilience. Both unbleached and bleached sea anemones had increased Symbiodiniaceae density and total chlorophyll when anemonefish were present, which is likely due to the nutrients excreted by the ectosymbiont17,42. Sea anemones hosting anemonefish have a distinct ecological advantage that will become increasingly important as sea temperatures continue to rise. Obligate symbioses and reliance on a specialised habitat can impose additional risks to both the habitat and the hosted organism during environmental variation45,46. However, here we clearly show how the anemonefish-sea anemone-Symbiodiniaceae association can be beneficial following bleaching.

In this study, Symbiodiniaceae density and total chlorophyll increased considerably for both unbleached and bleached E. quadricolor hosting the anemonefish A. akindynos. Similarly, for unbleached E. quadricolor, Symbiodiniaceae density increases when hosting A. bicinctus in the laboratory, and the sea anemone Heteractis magnifica grows faster when A. chrysopterus are present in the field17, 40,47. Additionally, we have shown that anemonefish facilitate bleaching resilience, as Symbiodiniaceae density and colour score showed full recovery in sea anemones hosting anemonefish (i.e. bleached with fish were statistically similar to the unbleached controls). Damselfish have been found to assist coral bleaching recovery by enhancing endosymbiont density and chlorophyll concentration6, as has heterotrophic feeding48,49,50. The facilitated recovery, both in this study and by Chase et al.6 may be enabled by fishes excreting waste products that are absorbed by the sea anemone and subsequently, their Symbiodiniaceae. The additional nutrients are likely to have increased endosymbiont asexual reproduction, leading to higher density13,17. Additionally, ad hoc observations showed that bleached sea anemones spent more time with their tentacles expanded when hosting anemonefish, which would enhance light interception and potentially benefit Symbiodiniaceae, facilitating recovery40. Interestingly, total chlorophyll was similar between the bleached and unbleached sea anemones at the start of the experiment, indicating bleaching occurred due to symbiont loss. The similarity in total chlorophyll among treatments is likely due to reduced intraspecific competition between the Symbiodiniaceae in the bleached sea anemones, which may have resulted in higher chlorophyll concentration per cell.

Here, bleaching recovery was dependent on the presence of anemonefish, with Symbiodiniaceae density in fish-hosting anemones being similar to that of the unbleached controls within 2 months, and colour score within 3.5 months. The total chlorophyll was considerably higher in the sea anemones occupied by fish by the end of our experiment. Although horizontal endosymbiont repopulation was not possible due to filtered and UV sterilised seawater used in this experiment, our findings are comparable to the rates observed for H. magnifica hosting A. chrysopterus in Moorea, French Polynesia38. In contrast, only partial recovery was recorded 2–4 months following bleaching of occupied Stichodactyla haddoni and H. crispa in Bootless Bay, Papua New Guinea, and E. quadricolor remained bleached after 6 months at Lizard Island, Australia, despite hosting anemonefish32, 36. These findings suggest bleaching recovery in sea anemones is likely to be species-specific, as well as influenced by local environmental conditions and biological factors both during and after bleaching events. In our experiment, nutrients concentrations may not have been equivalent to field conditions, thus altering recovery times. Additionally, recovery in the bleached sea anemones without anemonefish may have been possible if a longer time frame was provided, given Symbiodiniaceae density did slightly increase over 3.5 months.

We found E. quadricolor with and without anemonefish survived for extended periods in the laboratory following bleaching. While this was somewhat unexpected, survival is likely to be linked to bleaching severity and environmental variables such as water flow, light levels, and organic matter44,51,52,53. Thus, mortality is not constant among locations and events. For example, 5% of occupied S. haddoni and H. crispa at Bootless Bay died following three weeks of warming36, in comparison to 88% of occupied H. crispa at Sesoko Island, Japan, following 13 weeks of elevated temperatures during the 1998 mass bleaching event34.

For sea anemones with and without anemonefish, asexual reproduction via longitudinal fission appeared to be influenced by temperature. Previous studies have shown increased fission results from experimentally elevated temperatures in a range of non-host sea anemones54,55,56,57. In our experiment, fission occurred much more often in sea anemones with anemonefish, regardless of thermal exposure and bleaching status. Therefore, while temperature may have influenced fission, the presence of fish was the overriding causative factor. Similarly, increased fission has been documented in the field for unbleached H. magnifica with anemonefish58. Fish may accelerate fission by augmenting nutrition, as feeding has been shown to increase asexual reproduction54,59,60,61.

By elucidating a previously unknown benefit of the anemonefish-sea anemone-Symbiodiniaceae symbiosis, our findings add to the growing body of literature that shows interactive relationships can enhance resilience to climate change4,5,6,7,8. We found that bleached sea anemones with anemonefish were able to recover, whereas those without anemonefish did not. Given severe bleaching events are increasing in frequency10,62, and can result in decreased sea anemone and anemonefish abundance31,32,33,34, anemonefishes are likely to enhance host sea anemone survival as our oceans continue to warm. Symbioses between fishes, such as gobies and damselfish, and cnidarians that bleach are common on coral reefs63,64, and can also provide resilience to bleaching6. Therefore, while this study used the anemonefish-sea anemone symbiosis, the findings are not uniquely relevant to this model system. These results highlight the need to ensure symbioses are maintained and reinforce the importance of management and conservation efforts focusing on ecosystem, rather than single-species, approaches.


Collection and acclimation of Entacmaea quadricolor and Amphiprion akindynos

Entacmaea quadricolor (N = 48) that did not host anemonefish were collected from 13-m depth in July 2017 (austral winter) at North Solitary Island, Australia (29°55′54ʺ S, 153°23′21ʺ N). Unoccupied sea anemones were used to ensure the presence of anemonefish did not impact Symbiodiniaceae density before experimentation17, and to minimise potential adverse impacts to the anemonefish population at the collection location. As colour morph has been shown to influence bleaching susceptibility for this species44,65, all sea anemones had a green column, brown tentacles with green and white pigmentation at the tips and a brown oral disc. After collection, individuals were transported to the National Marine Science Centre (NMSC), Coffs Harbour, New South Wales, Australia, and kept in a 2000 L rectangular outdoor tank with ambient flow-through seawater (20.5 °C, reflecting temperature at the collection location, 8 L min−1) for 26 days. Light levels were reduced by 70% shade cloth to simulate conditions at the collection location. Water temperature within the outdoor tank was increased from 20.5 to 22 °C by ramping 0.5 °C every 2 days using thermostatically controlled heater-chiller units, reflecting summer temperatures experienced in the collection region. Sea anemones were kept at this temperature for 53 days and fed Melicertus plebejus (Eastern King Prawn, ~ 1 cm3) flesh fortnightly.

Amphiprion akindynos form a symbiotic relationship with E. quadricolor. These fish were collected as pairs consisting of one female and one male (N = 16 pairs, total length = 10.3 ± SE 0.18 cm) from North Solitary Island. Pairs were then transported to the NMSC and held at ambient temperature (20.5 °C) with flow-through seawater (200 mL min−1) in individual 42 L white plastic aquaria (432 mm long × 324 mm wide × 305 mm deep). Before the experiment commenced, terracotta pots were provided as habitat and fish were fed pellets (Hakari Marine A) twice daily. Fish were collected under a NSW Department of Primary Industries Scientific Collection Permit (P17/0042–1.1). Experimental protocols were carried out in accordance with NSW Animal Research Act (1985) and Regulation (2010), and approved by Southern Cross University Animal Care and Ethics Committee (Animal Research Authority 17/42).

Sea anemone bleaching

Sea anemones were divided equally between two 2,000 L tanks, and the temperature was increased to 27 °C over 24 h (0.5 °C.2 h−1) in one tank to induce thermal bleaching, whereas the other was maintained at 22 °C. The higher temperature aligns with future ocean temperature predictions66, in addition to bleaching thresholds found for E. quadricolor in this region44. These conditions were maintained for 48 days, during which the sea anemones were monitored with a CoralWatch Coral Health Chart to assess bleaching67,68. This chart uses a brightness/saturation score, with four colour hues (here, the E hue was used), each with a score ranging from one to six, with a two-point reduction indicating a significant loss of Symbiodiniaceae and chlorophyll a68. Colour score was determined halfway down the tentacle where host pigmentation was least likely to obscure the reading, and therefore the score would be more indicative of bleaching. After exposure to increased temperatures, Symbiodiniaceae density was 17,816 ± SE 3,995 per mg of host protein, and colour score was 1.8 ± 0.07 for the bleached sea anemones, in comparison to 672,141 ± 84,168 symbionts per mg of host protein and colour score of 5.1 ± 0.07 , for those maintained at 22 °C (i.e. unbleached). Therefore, Symbiodiniaceae remained present in all sea anemones, making vertical repopulation possible. While all sea anemones were a similar size before bleaching (tentacle crown diameter of 13.3 ± 0.3 cm), variation was apparent after thermal exposure (tentacle crown diameter in unbleached sea anemones was 14.9 ± 1.0 cm, and for the bleached sea anemones was 9.3 ± 0.5 cm).

Experimental conditions

Sea anemones were randomly placed into individual 42 L white plastic aquaria (432 mm long × 324 mm wide × 305 mm deep), divided evenly among four 2000 L water tables (2000 mm long × 1000 mm wide × 1000 mm deep). Initially, heated seawater was supplied to bleached sea anemones (27 °C, n = 24), and then gradually decreased to 23 °C over 24 h. Once the average summer temperature of 23 °C was reached, the experiment began, and therefore time 0 was 24 h post thermal bleaching. To reduce the likelihood of pathogens entering the experimental system and adversely affecting the anemonefish, filtered (50 µm) and UV sterilised (50 W) seawater was supplied (200 mL min−1) to all aquaria. Temperature and light intensity were recorded every 15 min, using 16 and 3 randomly placed loggers, respectively. Shade cloth was placed over the tanks to achieve light levels similar to field conditions. The maximum light intensity reached was 695.5 μmol photons m−2 s−1 (see Supplementary Information Fig. 1).


Sea anemones were randomly assigned to one of six treatments, each with eight replicates: (i) bleached with an anemonefish pair; (ii) unbleached with an anemonefish pair (one female, one male); (iii) bleached without anemonefish (bleached control); (iv) unbleached without anemonefish (unbleached control); (v) bleached without anemonefish but with fish food pellets added (bleached procedural control) and; (vi) unbleached without anemonefish but with fish food pellets added (unbleached procedural control). Amphiprion akindynos were fed pellets (Hakari Marine A) to satiety twice daily. Food was added at the opposite end of the aquaria to the sea anemone, and uneaten pellets were removed after 30 min. The procedural control also had inaccessible fish food pellets placed in the same location for an equal duration.

Food was also provided directly to the sea anemones to account for heterotrophic feeding in the field. Little information is available on the frequency or amount of feeding that would naturally occur for E. quadricolor. Therefore, a conservative approach was taken, with all sea anemones being fed M. plebejus flesh (~ 1 cm3) every four weeks.

Tentacle removal and processing

Tentacles were collected on days 0, 21, 49, 77 and 106 to determine host protein, Symbiodiniaceae density, and total chlorophyll concentration. If a sea anemone had split, samples were taken from each fragment and averaged. For each sea anemone, 3–4 tentacles were removed using dissection scissors and placed in a 10 mL centrifuge tube containing 4 mL of 0.4 μm filtered seawater. Samples were homogenised at 15,000 rpm. The homogenate was centrifuged at 4500 rpm for 15 min until the Symbiodiniaceae pellet separated from the sea anemone supernatant.

Host protein analysis

Host supernatant was removed, placed into 10 mL digestion vials and frozen at − 20 °C, then later analysed to determine protein content. The samples were transported on ice to the Environmental Analysis Laboratory, Southern Cross University, Australia. Once thawed, samples were diluted 100 times with ultrapure water, acidified with nitric acid digestion solution, and filtered with a 0.45 μm cellulose acetate filter. Nitrogen content (mg. L−1) was determined using Inductively Coupled Plasma Mass Spectrophotometry69, and converted to protein content by multiplying by 6.2570.

Symbiodiniaceae density

For each sample, the Symbiodiniaceae pellet was re-suspended in 4 mL of 0.4 μm filtered seawater and homogenised for 10 s at 15,000 rpm. Homogenate (1 mL) was placed into 1.5 mL microcentrifuge tubes to determine Symbiodiniaceae density. Using a haemocytometer, either 8 or 12 replicate counts were done per sample with either 5 or 25 fields per count, depending on cell density. More replicates and fields were used for low density (≤ 10 cells per field) counts to ensure accuracy. Counts were standardised against host protein.

Chlorophyll concentration

To determine total chlorophyll (chlorophyll a + c2), the remaining 3 mL of solution was re-centrifuged at 4500 rpm for 15 min, and the supernatant was discarded. The algal pellet was re-suspended in 4 mL of 90% acetone and kept for 24 h at 4 °C in the dark to avoid photodecomposition while exposed to this solvent. The suspension was centrifuged once more at 4500 rpm for 15 min. The supernatant was then placed into a cuvette and absorbance at 630, and 664 nm was measured on a Bibby Anadéo spectrophotometer. Total chlorophyll concentration was determined using the equations of Jeffrey and Humphrey71 and expressed in mg of host protein.

Visual observations

Colour score was recorded on days 1, 12, 25, 41, 60, 82 and 106 using a CoralWatch Coral Health Chart67,68. Three tentacles from each sea anemone were observed, and an average calculated for each individual. Sea anemones were monitored visually twice daily for survivorship and asexual reproduction via longitudinal fission.

Statistical analysis

Permutational Multivariate Analysis of Variance (PERMANOVA) in PRIMER v6 + PERMANOVA was conducted to determine statistical differences among treatments. Univariate resemblance matrices were generated using Euclidean Distance. Permutational Analysis of Multivariate Dispersion (PERMDISP) was used to test for significant deviation from the centroid, and if found, data were log (x + 1) transformed. As no significant effect was found with the nested tank factor, a one-way design was used comparing treatments. Within this design, a priori comparisons were set up to test for differences between the bleached control and bleached procedural control, and between the unbleached control and unbleached procedural control. For these tests, no statistically significant differences for Symbiodiniaceae density, total chlorophyll or colour score were found, and so the bleached control and bleached procedural control treatments were pooled, as were the unbleached control and unbleached procedural control treatments. Further comparisons of Symbiodiniaceae density, total chlorophyll and colour score were made to test the following hypotheses: values in bleached sea anemones with anemonefish were significantly greater than bleached controls (pooled); values in bleached sea anemones with anemonefish did not differ significantly from unbleached controls (pooled); values in unbleached sea anemones with anemonefish were significantly greater than bleached with anemonefish and; values in unbleached sea anemones with anemonefish were significantly greater than unbleached controls (pooled). All PERMANOVAs were tested using 4999 raw data permutations with Type III sum-of-squares. Outputs from the statistical analyses can be found in the results section of this manuscript and Supplementary Information Table 1.

Data availability

Data are available at


  1. Muscatine, L. & Porter, J. W. Reef corals: Mutualistic symbioses adapted to nutrient-poor environments. Bioscience 27, 454–460 (1977).

    Google Scholar 

  2. Smith, D. C. & Douglas, A. E. The Biology of Symbiosis (Edward Arnold Ltd., London, 1987).

    Google Scholar 

  3. Rao, H. Interorganizational Ecology: Haygreeva. In The Blackwell Companion to Organisations (ed. Baum, J. A.) 541–556 (Backwell, Oxford, 2017).

    Google Scholar 

  4. Martínez-García, L. B., De Deyn, G. B., Pugnaire, F. I., Kothamasi, D. & van der Heijden, M. G. Symbiotic soil fungi enhance ecosystem resilience to climate change. Glob. Chang. Biol. 23, 5228–5236 (2017).

    ADS  PubMed  PubMed Central  Google Scholar 

  5. Compant, S., Van Der Heijden, M. G. & Sessitsch, A. Climate change effects on beneficial plant–microorganism interactions. FEMS Microbiol. Ecol. 73, 197–214 (2010).

    CAS  PubMed  Google Scholar 

  6. Chase, T., Pratchett, M., Frank, G. & Hoogenboom, M. Coral-dwelling fish moderate bleaching susceptibility of coral hosts. PLoS ONE 13, e0208545 (2018).

    CAS  PubMed  PubMed Central  Google Scholar 

  7. Redman, R. S. et al. Increased fitness of rice plants to abiotic stress via habitat adapted symbiosis: A strategy for mitigating impacts of climate change. PLoS ONE 6, e14823 (2011).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  8. Stewart, H. L., Holbrook, S. J., Schmitt, R. J. & Brooks, A. J. Symbiotic crabs maintain coral health by clearing sediments. Coral Reefs 25, 609–615 (2006).

    ADS  Google Scholar 

  9. Pachauri, R. K. et al. Climate change 2014: Synthesis report. Contribution of Working Groups I, II and III to the fifth assessment report of the Intergovernmental Panel on Climate Change. (IPCC, Switzerland, 2014).

  10. Hoegh-Guldberg, O. Climate change, coral bleaching and the future of the world’s coral reefs. Mar. Freshw. Res. 50, 839–866 (1999).

    Google Scholar 

  11. Mieog, J. C. et al. The roles and interactions of symbiont, host and environment in defining coral fitness. PLoS ONE 4(7), e6364 (2009).

    ADS  PubMed  PubMed Central  Google Scholar 

  12. Davies, P. S. The role of zooxanthellae in the nutritional energy requirements of Pocillopora eydouxi. Coral Reefs 2, 181–186 (1984).

    ADS  Google Scholar 

  13. Cook, C., D’Elia, C. & Muller-Parker, G. Host feeding and nutrient sufficiency for zooxanthellae in the sea anemone Aiptasia pallida. Mar. Biol. 98, 253–262 (1988).

    CAS  Google Scholar 

  14. Roopin, M., Henry, R. P. & Chadwick, N. E. Nutrient transfer in a marine mutualism: Patterns of ammonia excretion by anemonefish and uptake by giant sea anemones. Mar. Biol. 154, 547–556 (2008).

    CAS  Google Scholar 

  15. Delia, C., Domotor, S. & Webb, K. Nutrient uptake kinetics of freshly isolated zooxanthellae. Mar. Biol. 75, 157–167 (1983).

    CAS  Google Scholar 

  16. Steen, R. G. & Muscatine, L. Low temperature evokes rapid exocytosis of symbiotic algae by a sea anemone. Biol. Bull. 172, 246–263 (1987).

    Google Scholar 

  17. Roopin, M. & Chadwick, N. E. Benefits to host sea anemones from ammonia contributions of resident anemonefish. J. Exp. Mar. Biol. Ecol. 370, 27–34 (2009).

    CAS  Google Scholar 

  18. Brown, B. E. Coral bleaching: Causes and consequences. Coral Reefs 16, 129–138 (1997).

    Google Scholar 

  19. Glynn, P. W. Widespread coral mortality and the 1982–83 El Niño warming event. Environ. Conserv. 11, 133–146 (1984).

    Google Scholar 

  20. McClanahan, T. R., Ateweberhan, M., Muhando, C. A., Maina, J. & Mohammed, M. S. Effects of climate and seawater temperature variation on coral bleaching and mortality. Ecol. Monogr. 77, 503–525 (2007).

    Google Scholar 

  21. Vinoth, R., Gopi, M., Kumar, T. T. A., Thangaradjou, T. & Balasubramanian, T. Coral reef bleaching at Agatti Island of Lakshadweep Atolls India. J. Ocean Univ. China 11, 105–110 (2012).

    ADS  Google Scholar 

  22. Hughes, T. P. et al. Global warming transforms coral reef assemblages. Nat. 556, 492–496 (2018).

    ADS  CAS  Google Scholar 

  23. Death, G., Fabricius, K. E., Sweatman, H. & Puotinen, M. The 27-year decline of coral cover on the Great Barrier Reef and its causes. Proc. Natl. Acad. Sci. 109, 17995–17999 (2012).

    ADS  CAS  Google Scholar 

  24. Hughes, T. P. Catastrophes, phase shifts, and large-scale degradation of a Caribbean coral reef. Science 265, 1547–1551 (1994).

    ADS  CAS  PubMed  Google Scholar 

  25. McManus, J. W. & Polsenberg, J. F. Coral–algal phase shifts on coral reefs: Ecological and environmental aspects. Prog. Oceanogr. 60, 263–279 (2004).

    ADS  Google Scholar 

  26. Hughes, T. P., Graham, N. A., Jackson, J. B., Mumby, P. J. & Steneck, R. S. Rising to the challenge of sustaining coral reef resilience. Trends Ecol. Evol. 25, 633–642 (2010).

    PubMed  Google Scholar 

  27. Garpe, K. C., Yahya, S. A., Lindahl, U. & Öhman, M. C. Long-term effects of the 1998 coral bleaching event on reef fish assemblages. Mar. Ecol. Prog. Ser. 315, 237–247 (2006).

    ADS  Google Scholar 

  28. Pratchett, M. S. et al. Effects of climate-induced coral bleaching on coral-reef fishes—ecological and economic consequences. Oceanogr. Mar. Biol. 46, 257–302 (2008).

    Google Scholar 

  29. Pratchett, M. S., Hoey, A. S., Wilson, S. K., Messmer, V. & Graham, N. A. Changes in biodiversity and functioning of reef fish assemblages following coral bleaching and coral loss. Divers. 3, 424–452 (2011).

    Google Scholar 

  30. Dunn, D. F. The clownfish sea anemones: Stichodactylidae (Coelenterata: Actiniaria) and other sea anemones symbiotic with pomacentrid fishes. Trans. Am. Philos. Soc. 71, 3–115 (1981).

    Google Scholar 

  31. Jones, A., Gardner, S. & Sinclair, W. Losing “Nemo”: Bleaching and collection appear to reduce inshore populations of anemonefishes. J. Fish Biol. 73, 753–761 (2008).

    Google Scholar 

  32. Scott, A. & Hoey, A. S. Severe consequences for anemonefishes and their host sea anemones during the 2016 bleaching event at Lizard Island, Great Barrier Reef. Coral Reefs 36, 873–873 (2017).

    ADS  Google Scholar 

  33. Hobbs, J. P. A. et al. Taxonomic, spatial and temporal patterns of bleaching in anemones inhabited by anemonefishes. PLoS ONE 8, e70966 (2013).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  34. Hattori, A. Small and large anemonefishes can coexist using the same patchy resources on a coral reef, before habitat destruction. J. Anim. Ecol. 71, 824–831 (2002).

    Google Scholar 

  35. Weis, V. M. Cellular mechanisms of Cnidarian bleaching: Stress causes the collapse of symbiosis. J. Exp. Biol. 211, 3059–3066 (2008).

    CAS  PubMed  Google Scholar 

  36. Saenz-Agudelo, P., Jones, G., Thorrold, S. & Planes, S. Detrimental effects of host anemone bleaching on anemonefish populations. Coral Reefs 30, 497–506 (2011).

    ADS  Google Scholar 

  37. Lönnstedt, O. M. & Frisch, A. J. Habitat bleaching disrupts threat responses and persistence in anemonefish. Mar. Ecol. Prog. Ser. 517, 265–270 (2014).

    ADS  Google Scholar 

  38. Beldade, R., Blandin, A., O’Donnell, R. & Mills, S. C. Cascading effects of thermally-induced anemone bleaching on associated anemonefish hormonal stress response and reproduction. Nat. Commun. 8, 716 (2017).

    ADS  PubMed  PubMed Central  Google Scholar 

  39. Hoegh-Guldberg, O. & Smith, G. J. Influence of the population density of zooxanthellae and supply of ammonium on the biomass and metabolic characteristics of the reef corals Seriatopora hystrix and Stylophora pistillata. Mar. Ecol. Prog. Ser. 2, 173–186 (1989).

    ADS  Google Scholar 

  40. Holbrook, S. J. & Schmitt, R. J. Growth, reproduction and survival of a tropical sea anemone (Actiniaria): Benefits of hosting anemonefish. Coral Reefs 24, 67–73 (2005).

    Google Scholar 

  41. Porat, D. & Chadwick-Furman, N. Effects of anemonefish on giant sea anemones: Expansion behavior, growth, and survival. Hydrobiologia 530, 513–520 (2004).

    Google Scholar 

  42. Cleveland, A., Verde, E. A. & Lee, R. W. Nutritional exchange in a tropical tripartite symbiosis: Direct evidence for the transfer of nutrients from anemonefish to host anemone and zooxanthellae. Mar. Biol. 158, 589–602 (2011).

    Google Scholar 

  43. Fautin, D. G. & Allen, G. R. Field Guide to Anemonefishes and Their Host Sea Anemones (Western Australian Museum, Perth, 1992).

    Google Scholar 

  44. Hill, R. & Scott, A. The influence of irradiance on the severity of thermal bleaching in sea anemones that host anemonefish. Coral Reefs 31, 273–284 (2012).

    ADS  Google Scholar 

  45. Roughgarden, J. Evolution of marine symbiosis—a simple cost-benefit model. Ecology 56, 1201–1208 (1975).

    Google Scholar 

  46. Hobbs, J., Neilson, J. & Gilligan, J. Distribution, abundance, habitat association and extinction risk of marine fishes endemic to the Lord Howe Island region (Report to Lord Howe Island Marine Park (James Cook University, Townsville, 2009).

    Google Scholar 

  47. Porat, D. & Chadwick-Furman, N. Effects of anemonefish on giant sea anemones: Ammonium uptake, zooxanthella content and tissue regeneration. Mar. Freshw. Behav. Physiol. 38, 43–51 (2005).

    CAS  Google Scholar 

  48. Grottoli, A. G., Rodrigues, L. J. & Palardy, J. E. Heterotrophic plasticity and resilience in bleached corals. Nature 440, 1186–1189 (2006).

    ADS  CAS  Google Scholar 

  49. Borell, E. M. & Bischof, K. Feeding sustains photosynthetic quantum yield of a scleractinian coral during thermal stress. Oecologia 157, 593 (2008).

    ADS  PubMed  Google Scholar 

  50. Borell, E. M., Yuliantri, A. R., Bischof, K. & Richter, C. The effect of heterotrophy on photosynthesis and tissue composition of two scleractinian corals under elevated temperature. J. Exp. Mar. Biol. Ecol. 364, 116–123 (2008).

    Google Scholar 

  51. Nakamura, T. & Van Woesik, R. Water-flow rates and passive diffusion partially explain differential survival of corals during the 1998 bleaching event. Mar. Ecol. Prog. Ser. 212, 301–304 (2001).

    ADS  Google Scholar 

  52. Gleason, D. F. & Wellington, G. M. Ultraviolet radiation and coral bleaching. Nature 365, 836 (1993).

    ADS  Google Scholar 

  53. Zepp, R. G. et al. Spatial and temporal variability of solar ultraviolet exposure of coral assemblages in the Florida Keys: Importance of colored dissolved organic matter. Limnol. Oceanogr. 53, 1909–1922 (2008).

    ADS  CAS  Google Scholar 

  54. Minasian, L. L. Jr. The relationship of size and biomass to fission rate in a clone of the sea anemone, Haliplanella luciae (Verrill). J. Exp. Mar. Biol. Ecol. 58, 151–162 (1982).

    Google Scholar 

  55. Miyawaki, M. Temperature as a factor influencing upon the fission of the orange-striped sea-anemone, Diadumene luciae. Zool. 11, 77–80 (1952).

    Google Scholar 

  56. Atoda, K. Pedal laceration of the sea anemone, Haliplanella luciae. Pub. Seto Mar. Biol. Lab. 20, 299–313 (1973).

    Google Scholar 

  57. Minasian, L. L. Jr. & Mariscal, R. N. Characteristics and regulation of fission activity in clonal cultures of the cosmopolitan sea anemone, Haliplanella luciae (Verrill). Biol. Bull. 157, 478–493 (1979).

    PubMed  Google Scholar 

  58. Holbrook, S. J., Brooks, A. J., Schmitt, R. J. & Stewart, H. L. Effects of sheltering fish on growth of their host corals. Mar. Biol. 155, 521–530 (2008).

    Google Scholar 

  59. Johnson, L. L. & Shick, J. M. Effects of fluctuating temperature and immersion on asexual reproduction in the intertidal sea anemone Hauplanella luciae (Verrill) in laboratory culture. J. Exp. Mar. Biol. Ecol. 28, 141–149 (1977).

    Google Scholar 

  60. Hand, C. & Uhlinger, K. R. Asexual reproduction by transverse fission and some anomalies in the sea anemone Nematostella vectensis. Invertebr. Biol. 2, 9–18 (1995).

    Google Scholar 

  61. Tsuchida, C. B. & Potts, D. C. The effects of illumination, food and symbionts on growth of the sea anemone Anthopleura elegantissima (Brandt, 1835). II. Clonal growth. J. Exp. Mar. Biol. Ecol. 183, 243–258 (1994).

    Google Scholar 

  62. Hughes, T. P. et al. Global warming and recurrent mass bleaching of corals. Nature 543, 373–377 (2017).

    ADS  CAS  PubMed  Google Scholar 

  63. Holbrook, S. J., Forrester, G. E. & Schmitt, R. J. Spatial patterns in abundance of a damselfish reflect availability of suitable habitat. Oecologia 122, 109–120 (2000).

    ADS  CAS  PubMed  Google Scholar 

  64. Munday, P. L. Interactions between habitat use and patterns of abundance in coral-dwelling fishes of the genus Gobiodon. Environ. Biol. Fish. 58, 355–369 (2000).

    Google Scholar 

  65. Pontasch, S. et al. Photochemical efficiency and antioxidant capacity in relation to Symbiodinium genotype and host phenotype in a symbiotic cnidarian. Mar. Ecol. Prog. Ser. 516, 195–208 (2014).

    ADS  CAS  Google Scholar 

  66. IPCC. Climate Change 2014–Impacts, Adaptation and Vulnerability: Regional Aspect (Cambridge University Press, Cambridge, 2014).

    Google Scholar 

  67. Siebeck, U., Marshall, N., Klüter, A. & Hoegh-Guldberg, O. Monitoring coral bleaching using a colour reference card. Coral Reefs 25, 453–460 (2006).

    ADS  Google Scholar 

  68. Marshall, N. J., Kleine, D. A. & Dean, A. J. CoralWatch: Education, monitoring, and sustainability through citizen science. Front Ecol Environ 10, 332–334 (2012).

    Google Scholar 

  69. Association, A. P. H. Standard Methods for the Examination of Water and Wastewater (American Public Health Association, Washington, 2005).

    Google Scholar 

  70. AOAC. Official Methods of Analysis of AOAC International (Association of Official Analytical Chemists, Rockville, 2000).

    Google Scholar 

  71. Jeffrey, S. T. & Humphrey, G. F. New spectrophotometric equations for determining chlorophylls a, b, c1 and c2 in higher plants, algae and natural phytoplankton. Biochemie und physiologie der pflanzen 167, 191–194 (1974).

    Google Scholar 

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Thank you to Dive Quest, C. Holloway, A. King, G. Foley, D. Eggeling, J. Daley, B. Chen, H. Malcolm, M. Nimbs, S. Soule and G. Nanninga for technical and logistical support. Assistance with experiment maintenance was provided by A. Rodríguez, P. Gomez, R. Torres, and C. Catarino. This work was supported by grants from the National Science Foundation and National Geographic.

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Experimental design: A.S., R.H., S.H.P., B.P.K. and D.L.D.; data collection: S.H.P., N.J.F. and A.S.; data analysis: S.H.P., B.P.K, R.H. and A.S.; data interpretation: S.H.P., A.S., R.H. and D.L.D.; main text: S.H.P., and A.S. All authors edited the manuscript.

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Correspondence to Anna Scott.

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Pryor, S.H., Hill, R., Dixson, D.L. et al. Anemonefish facilitate bleaching recovery in a host sea anemone. Sci Rep 10, 18586 (2020).

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