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Does environmental context influence macroalgal community composition on artificial structures?

Authors:

Abstract

Artificial structures tend to support less diverse assemblages than natural hard substrata, but it is as yet unclear how this effect varies with environmental context. Here macroalgal assemblages were compared between artificial and natural substrata in different environmental contexts within the Irish Sea. We find no differences in macroalgal community structure between natural and artificial structures in any given environmental context. In contrast, we found coralline species to be significantly more abundant on natural substrata. Community composition differed in two contexts, between estuarine and marine sites, and between sites with different degrees of urban influence. We propose that these differences may be due to the presence and abundances of 'thick leathery' species.
DOES ENVIRONMENTAL CONTEXT INFLUENCE MACROALGAL COMMUNITY COMPOSITION ON
ARTIFICIAL STRUCTURES ?
Veronica Farrugia Drakard
*, Paul Brooks
, Ally Evans
, Tasman Crowe
and
Ecostructure WP2 Partners
University College Dublin
-
veronica.farrugiadrakard@ucdconnect.ie
IBERS, Aberystwyth University, UK
http://www.ecostructureproject.eu/
Abstract
Artificial structures tend to support less diverse assemblages than natural hard substrata, but it is as yet unclear how this effect
varies with environmental context. Here macroalgal assemblages were compared between artificial and natural substrata in
different environmental contexts within the Irish Sea. We find no differences in macroalgal community structure between natural
and artificial structures in any given environmental context. In contrast, we found coralline species to be significantly more
abundant on natural substrata. Community composition differed in two contexts, between estuarine and marine sites, and between
sites with different degrees of urban influence. We propose that these differences may be due to the presence and abundances of
thick leathery
species.
Keywords: North Atlantic, Algae, Biodiversity, Coastal systems, Rocky shores
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Artificial infrastructure has become a significant component of coastal and
marine systems, primarily due to accelerated urbanisation [1]. This increase
has major implications for coastal biodiversity, as biotic community
composition differs between artificial and natural substrata [2]. The eco-
engineering approach, which applies ecological principles to the design of
artificial infrastructure, is likely to play a significant role in future strategies to
incorporate ecologically
-sensitive design into marine developments. As
primary producers and habitat providers, seaweeds are integral to both the
physical and trophic structure of many shallow-water marine systems.
Variation in environmental conditions can alter both the species present and
their responses to microhabitats [3]. The aim of this study was therefore to
investigate how environmental context influences macroalgal community
composition on artificial and natural substrata along Irish and Welsh coasts.
We selected 54 sites around the Irish Sea for sampling, 30 along the Irish coast
and 24 along the Welsh coast. These consisted of both natural and artificial
substrata, and were characterised in terms of their environmental (
marine
vs.
estuarine’) and anthropogenic contexts (urban vs. low urban vs.
rural
).
Ten 25 cm x 25 cm quadrats were deployed at all sites and the abundances of
all macroalgal species present were recorded as percentage cover. Three-way
PERMANOVA and SIMPER procedures were used to characterise patterns in
macroalgal communities between sites.
Contrary to expectation, macroalgal abundances on artificial and natural
substrata did not differ (p = 0.15). There was no evidence of any effect of
environmental or anthropogenic context. There was a significant difference in
macroalgal abundances between
marine
and estuarine sites (F = 9.55, p <
0.05, df = 1), which was due to Ascophyllum nodosum predominating at
estuarine sites and Fucus vesiculosus predominating at marine sites (Table 1).
There were also significant differences between sites with different degrees of
urban influence (F = 3.04, p < 0.05, df = 2), once again due to A. nodosum and
F. vesiculosus, both of which were present at significantly higher abundances
in
rural
locations compared to more urban areas (Table 1).
Coralline species were consistently more abundant on natural rather than
artificial substrata (F = 10.81, p < 0.05, df = 1). These tend to display low
rates of growth and may be unable to establish stable populations under
conditions of frequent disturbance. This has implications for succession on
artificial structures, as coralline species have been shown to influence
recruitment [4] and may provide a more suitable substrate for settlement of
later macroalgal colonists [5].
There was considerable variation among sites in all analyses and we will
undertake statisticial modelling to investigate associated environmental factors.
Although percentage cover is a robust measure widely utilised in this field, it
tells us little about the health and persistence of seaweed populations;
therefore, we are also undertaking a more detailed investigation focused on the
biological function of key habitat providers. The ultimate aim of the work is to
inform effective design of eco
-engineering solutions to enhance biodiversity on
coastal infrastructure.
Tab. 1. SIMPER results showing taxa cumulatively contributing up to 50% to
the dissimilarity between groups tested. Abundances are square root
transformed.
Acknowledgements This research has been funded in part by the Irish
Research Council under the Government of Ireland Postgraduate Programme,
co
-funded by the Environmental Protection Agency. This work was
undertaken as part of the Ecostructure project, which was part-funded by the
European Regional Development Fund (ERDF) Ireland Wales Cooperation
Programme 2014
– 2020.
References
1 - Brook T.W., Gilby B.L., Olds A.D., Connolly R.M., Henderson C.J. and
Schlacher T.A. (2018). The effects of shoreline armouring on estuarine fish are
contingent upon the broader urbanisation context. Marine Ecology Progress
Series, 605, 195 – 206.
2 - Mineur F., Cook E.J., Minchin D., Bohn K., MacLeod A. and Maggs C.A.
(2012). Changing coasts: marine aliens and artificial structures. Oceanography
and Marine Biology: An Annual Review, 50, 189 – 234.
3 - Strain E.M.A., Olabarria C., Mayer-Pinto M., Cumbo V., Morris R.L.,
Bugnot A.B., ... and Bishop M.J. (2017). Eco-
engineering urban infrastructure
for marine and coastal biodiversity: which interventions have the greatest
ecological benefit?
Journal of Applied Ecology
. DOI: 10.1111/1365-
2664.12961.
4 - McCoy S.J. and Kamenos N.A. (2015). Coralline algae (Rhodophyta) in a
changing world: integrating ecological, physiological, and geochemical
responses to global change.
Journal of Phycology
, 51, 6 – 24.
5 - Asnaghi V., Thrush S.F., Hewitt J.E., Mangialajo L., Cattaneo-Vietti R. and
Chiantore M. (2015). Colonisation processes and the role of coralline algae in
rocky shore community dynamics. Journal of Sea Research, 95, 132 – 138.
219 Rapp. Comm. int. Mer Médit., 42, 2019
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Article
Full-text available
Coralline algae are globally distributed benthic primary producers that secrete calcium carbonate skeletons. In the context of ocean acidification, they have received much recent attention due to the potential vulnerability of their high-Mg calcite skeletons and their many important ecological roles. Herein, we summarize what is known about coralline algal ecology and physiology, providing context to understand their responses to global climate change. We review the impacts of these changes, including ocean acidification, rising temperatures, and pollution, on coralline algal growth and calcification. We also assess the ongoing use of coralline algae as marine climate proxies via calibration of skeletal morphology and geochemistry to environmental conditions. Finally, we indicate critical gaps in our understanding of coralline algal calcification and physiology and highlight key areas for future research. These include analytical areas that recently have become more accessible, such as resolving phylogenetic relationships at all taxonomic ranks, elucidating the genes regulating algal photosynthesis and calcification, and calibrating skeletal geochemical metrics, as well as research directions that are broadly applicable to global change ecology, such as the importance of community-scale and long-term experiments in stress response.
Article
Full-text available
Marine aliens are non-native species that have been transported across major geographi-cal barriers by human activities, involving vectors that move propagules along pathways. Species may also be newly observed in a geographical area due to range shifts, generally in association with climate change. Artificial structures are considered to be either man-made materials or natural materials shaped or displaced to serve a specific function for human activities. All types of artificial structures are currently increasing dramatically in coastal zones due to increasing human popula-tions on coastlines. Most of the significant marine vectors and pathways involve mobile artificial structures and are reviewed here. These include shipping (ballast water and hull fouling) and aqua-culture, including stock transfer and unintentional introductions, all of which can move species into new biogeographical provinces. Some types of structures frequently move long distances but have low fouling loads (e.g., commercial shipping), whereas others (e.g., barges and pontoons) can be hyperfouled due to long stationary periods such that when moved they transport mature fouling communities. We also examine the presence of alien marine species on static (immobile) artificial structures, which support different communities from those on natural hard substrata. We consider the role of these structures, such as coastal defences, artificial reefs, and offshore platforms, in the dispersal and abundance of alien species. Marinas include both mobile and immobile structures and are apparently particularly favourable habitats for many aliens. For example, in coastal North America approximately 90% of the alien species inhabiting hard substrata have been reported from docks and marinas. Detailed case studies of alien marine species (two seaweeds and four inverte-brates) are provided, with an analysis of their origin, vectors of transport, habitat in the introduced range, and potential impact. Although there are exceptions, a large majority of marine alien species seem to be associated, at least for some of the time, with artificial structures. It is clear that artificial structures can pave the way and act as stepping stones or even corridors for some marine aliens, as do urban areas, roads and riparian environments in terrestrial ecosystems. The observed acceleration of spread rates for marine invasions over the course of the last two centuries may partly be a result of the increase of artificial structures in coastal environments coupled with greater activity of vectors.
Article
Recovery from disturbance is an important attribute of community dynamics. Temperate rocky shores will experience increases in both the type and intensity of impacts under future expected global change. To gauge the community response to these potential changes in the disturbance regime it is important to assess space occupancy and the temporal dynamics of key species over the recovery process. We experimentally disturbed replicated 1 m2 plots in the lower intertidal at 5 sites along the Ligurian rocky coast (North-western Mediterranean) and assessed early succession processes over 18 months. To identify colonization processes and role of key species in affecting species richness on recovery trajectories, we monitored species composition at the cm-scale along fixed transects within the plots. Our results highlighted the role of a limited number of taxa in driving the recovery of species richness across sites, despite site variation in community composition. Settlement of new propagules and overgrowth were the principal pathway of space occupancy. We detected an important role for coralline algae, particularly the articulated Corallina elongata, in promoting the colonization of a diverse range of colonists. The present study highlights the important role played by calcifying coralline macroalgae as substrate providers for later colonists, favouring recovery of biodiversity after disturbance. This pivotal role may be compromised in a future scenario of elevated cumulative disturbance, where ocean acidification will likely depress the role of coralline algae in recovery, leading to a general loss in biodiversity and community complexity.
Eco-engineering urban infrastructure for marine and coastal biodiversity: which interventions have the greatest ecological benefit
  • E M A Strain
  • C Olabarria
  • M Mayer-Pinto
  • V Cumbo
  • R L Morris
  • A B Bugnot
  • . . Bishop
Strain E.M.A., Olabarria C., Mayer-Pinto M., Cumbo V., Morris R.L., Bugnot A.B.,... and Bishop M.J. (2017). Eco-engineering urban infrastructure for marine and coastal biodiversity: which interventions have the greatest ecological benefit? Journal of Applied Ecology. DOI: 10.1111/1365-2664.12961.