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Comparative Study
. 2019 May 21;116(21):10586-10591.
doi: 10.1073/pnas.1721415116. Epub 2019 May 6.

Using naturally occurring climate resilient corals to construct bleaching-resistant nurseries

Affiliations
Comparative Study

Using naturally occurring climate resilient corals to construct bleaching-resistant nurseries

Megan K Morikawa et al. Proc Natl Acad Sci U S A. .

Abstract

Ecological restoration of forests, meadows, reefs, or other foundational ecosystems during climate change depends on the discovery and use of individuals able to withstand future conditions. For coral reefs, climate-tolerant corals might not remain tolerant in different environments because of widespread environmental adjustment of coral physiology and symbionts. Here, we test if parent corals retain their heat tolerance in nursery settings, if simple proxies predict successful colonies, and if heat-tolerant corals suffer lower growth or survival in normal settings. Before the 2015 natural bleaching event in American Samoa, we set out 800 coral fragments from 80 colonies of four species selected by prior tests to have a range of intraspecific natural heat tolerance. After the event, nursery stock from heat-tolerant parents showed two to three times less bleaching across species than nursery stock from less tolerant parents. They also retained higher individual genetic diversity through the bleaching event than did less heat-tolerant corals. The three best proxies for thermal tolerance were response to experimental heat stress, location on the reef, and thermal microclimate. Molecular biomarkers were also predictive but were highly species specific. Colony genotype and symbiont genus played a similarly strong role in predicting bleaching. Combined, our results show that selecting for host and symbiont resilience produced a multispecies coral nursery that withstood multiple bleaching events, that proxies for thermal tolerance in restoration can work across species and be inexpensive, and that different coral clones within species reacted very differently to bleaching.

Keywords: American Samoa; bleaching; climate change; coral resilience; restoration.

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Conflict of interest statement

The authors declare no conflict of interest.

Figures

Fig. 1.
Fig. 1.
(Upper) Forty corals from the HVP (red border) and 40 from the MVP (orange border) colored by time spent above 31 °C from December 2014 to April 2015 (austral summer). (Lower) Thermal tolerance (relative chlorophyll retained after a single day, species-specific heat stress) tends to be higher in corals from the HVP. Corals are arranged in ascending order of chlorophyll retention for the four species. Error bars represent SD across four paired replicates per colony.
Fig. 2.
Fig. 2.
(A) Average temperature in the HVP, the MVP, and the transplant site in Sili with observed natural bleaching marked in the red box. The gray line marks the expected threshold bleaching temperature. (B) Visual bleaching severity of nubbins in the nursery partitioned using the three simplest proxies for predicted resilience. Labels on the predicted resilient or vulnerable stocks axis are as follows: (A, in blue lettering) corals from the HVP; (B, in blue lettering) top 10 experimental stress performers; (C in blue lettering) hottest extreme microclimates and the corresponding predicted vulnerable stocks: (a) corals from the MVP; (b) bottom 10 experimental stress performers; and (c) coolest extreme microclimates.
Fig. 3.
Fig. 3.
Correlations between the average bleaching severity of replicate nursery nubbins in Sili versus the average bleaching severity of their parent genotypes in their original habitats. Photograph demonstrates severely bleached A. gemmifera next to nonbleached nubbins.
Fig. 4.
Fig. 4.
Average percent bleaching across four species in the Sili nursery after the 2015 natural bleaching event. Bleaching of nubbins that came from parents from the HVP (red) was two- to threefold lower than for nubbins with parents from the MVP (orange).

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