TY - JOUR
T1 - Resistance, Extinction and Everything in Between - The Diverse Responses of Seaweeds to Marine Heatwaves
AU - Straub, Sandra C.
AU - Wernberg, Thomas
AU - Thomsen, Mads S.
AU - Moore, Pippa
AU - Burrows, Michael T.
AU - Harvey, Benjamin
AU - Smale, Dan A.
N1 - Funding Information:
This contribution is an outcome from the working group “MHWs 2 – Biological implications of heatwaves for marine ecosystems” hosted at the Marine Biological Association of the United Kingdom (Plymouth, United Kingdom) by DS and TW. The working group received support from a University of Western Australia Research Collaboration Award, a UWA School of Plant Biology synthesis grant, a Natural Environment Research Council (United Kingdom) International Opportunity Fund (NE/N00678X/1), and the ARC Centre of Excellence for Climate System Science (ARCCSS). SS was supported by an Australian Government Research Training Program (RTP) Scholarship, TW by ARC grant numbers FT110100174 and DP170100023, DS by NERC IRF NE/K008439/1, PM by a Marie Curie Career Integration Grant (PCIG10-GA-2011-303685) and a Natural Environment Research Council (United Kingdom) Grant (NE/J024082/1), and MT by Brian Mason.
Publisher Copyright:
© Copyright © 2019 Straub, Wernberg, Thomsen, Moore, Burrows, Harvey and Smale.
PY - 2019/12/13
Y1 - 2019/12/13
N2 - Globally, anomalously warm temperature events have increased by 34% in frequency and 17% in duration from 1925 to 2016 with potentially major impacts on coastal ecosystems. These “marine heatwaves” (MHWs) have been linked to changes in primary productivity, community composition and biogeography of seaweeds, which often control ecosystem function and services. Here we review the literature on seaweed responses to MHWs, including 58 observations related to resistance, bleaching, changes in abundance, species invasions and local to regional extinctions. More records existed for canopy-forming kelps and bladed and filamentous turf-forming seaweeds than for canopy-forming fucoids, geniculate coralline turf and crustose coralline algae. Turf-forming seaweeds, especially invasive seaweeds, generally increased in abundance after a MHW, whereas native canopy-forming kelps and fucoids typically declined in abundance. We also found four examples of regional extinctions of kelp and fucoids following specific MHWs, events that likely have long term consequences for ecological structure and functioning. Although a relatively small number of studies have described impacts of MHWs on seaweed, the broad range of documented responses highlights the necessity of better baseline information regarding seaweed distributions and performance, and the need to study specific characteristics of MHWs that affect the vulnerability and resilience of seaweeds to these increasingly important climatic perturbations. A major challenge will be to disentangle impacts caused by the extreme temperature increases of MHWs itself from co-occurring potential stressors including altered current patterns, increasing herbivory, changes in water clarity and nutrient content, solar radiation and desiccation stress in the intertidal zone. With future increases anticipated in the intensity, duration and frequencies of MHWs, we expect to see more replacements of large long-lived habitat forming seaweeds with smaller ephemeral seaweeds, reducing the habitat structure and effective services seaweed-dominated reefs can provide
AB - Globally, anomalously warm temperature events have increased by 34% in frequency and 17% in duration from 1925 to 2016 with potentially major impacts on coastal ecosystems. These “marine heatwaves” (MHWs) have been linked to changes in primary productivity, community composition and biogeography of seaweeds, which often control ecosystem function and services. Here we review the literature on seaweed responses to MHWs, including 58 observations related to resistance, bleaching, changes in abundance, species invasions and local to regional extinctions. More records existed for canopy-forming kelps and bladed and filamentous turf-forming seaweeds than for canopy-forming fucoids, geniculate coralline turf and crustose coralline algae. Turf-forming seaweeds, especially invasive seaweeds, generally increased in abundance after a MHW, whereas native canopy-forming kelps and fucoids typically declined in abundance. We also found four examples of regional extinctions of kelp and fucoids following specific MHWs, events that likely have long term consequences for ecological structure and functioning. Although a relatively small number of studies have described impacts of MHWs on seaweed, the broad range of documented responses highlights the necessity of better baseline information regarding seaweed distributions and performance, and the need to study specific characteristics of MHWs that affect the vulnerability and resilience of seaweeds to these increasingly important climatic perturbations. A major challenge will be to disentangle impacts caused by the extreme temperature increases of MHWs itself from co-occurring potential stressors including altered current patterns, increasing herbivory, changes in water clarity and nutrient content, solar radiation and desiccation stress in the intertidal zone. With future increases anticipated in the intensity, duration and frequencies of MHWs, we expect to see more replacements of large long-lived habitat forming seaweeds with smaller ephemeral seaweeds, reducing the habitat structure and effective services seaweed-dominated reefs can provide
KW - temperature extremes
KW - temperature anomalies
KW - climate variability
KW - extreme climatic events
KW - macroalgae
KW - foundation species
KW - habitat formers
KW - range contraction
UR - http://www.scopus.com/inward/record.url?scp=85077303827&partnerID=8YFLogxK
U2 - 10.3389/fmars.2019.00763
DO - 10.3389/fmars.2019.00763
M3 - Review Article
SN - 2296-7745
VL - 6
JO - Frontiers in Marine Science
JF - Frontiers in Marine Science
M1 - 763
ER -