Elsevier

Chemosphere

Volume 263, January 2021, 128276
Chemosphere

Sea urchin repelling Tannin– FeIII complex coating for ocean macroalgal afforestation

https://doi.org/10.1016/j.chemosphere.2020.128276Get rights and content

Highlights

  • TA-FeIII coating on marine substrate is a practical solution for urchin barren.

  • Tannin-FeIII coating exhibited the ability to repel sea urchins.

  • Sea urchin avoidance responses were positively related to the TA-FeIII concentration.

  • The repelling ability of Tannin-FeIII was also evident in ocean filed experiments.

Abstract

Intense seaweed grazing by sea urchins has destroyed kelp forests and accelerated the transformation of these forests into barren areas known as urchin barrens. Once the sea urchins occupy the barren ground, it becomes more challenging to restore the kelp forests. Although phlorotannin, a primary herbivore defense chemical secreted by kelp, has been reported to discourage feeding activities of marine herbivores but the direct application of naturally extracted phlorotannin does not effectively repel sea urchins. In this study, we applied a simple and green Tannin-FeIII (TA-FeIII) coating on substrates as a sea urchin repellent using a cheap, ecofriendly tannin (TA) obtained from biomass as an alternative to phlorotannin. In a model aquarium experiment, most of the sea urchins (Anthocidaris crassispina) in the tank evaded the TA-FeIII-coated substrates. In field tests with 300 sea urchins, the majority of sea urchins could not crawl over the TA-FeIII-coated rope for more than 2 h in contrast to the control group. Hence, the safety, cost-effectiveness, and scalability of the TA-FeIII coating make it a practical candidate to protect the kelp ecosystem from sea urchins.

Graphical abstract

Graphical abstract: Schematic image showing the TA-FeIII complex coating on a target substrate and a possible repellent mechanism of the TA-FeIII complex.

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Introduction

Macroalgal forests (kelp forests), a fertile habitat for a variety of marine organisms and a carbon dioxide sequestration site in marine ecosystems, have been disrupted off the coasts of east Asia, Australia, northern Europe, and north America due to climate change, ocean warming, and ocean acidification (Rosenzweig et al., 2008;Wernberg et al., 2012; Halpern et al., 2008). In addition, significant seaweed grazing by sea urchins and competition with calcified coralline algae have seriously disrupted the kelp forests (Steneck et al., 2002;Ling, 2009; Harrold and Pearse, 1987;Reed et al., 2006). Due to the negative effects of sea urchins and calcified coralline algae, these forests have been subsequently transformed into a barren land, and the restoration of these regions has become increasingly challenging (Wright et al., 2005;Gagnon et al., 2006). These areas are called urchin barrens because only sea urchins remain on a seafloor devoid of vegetation. Given the importance of the kelp forest to marine ecosystems, attempts to restore kelp forests have been made in America, Europe, Australia and Asia, but a practical solution relieving the damage of the urchin barrens has not been reported to date (Campbell et al., 2014;Galasso, 2015;Shear et al., 2012; Smith et al., 2004;Jung and Kim et al., 2020). Phlorotannin (Fig. 1b), a polyphenolic molecule secreted from most seaweed species, has been suggested as a repellent of marine herbivores, including the sea urchins. In recent decades, phlorotannin has exhibited deterrent effects to marine herbivory animals. Phlorotannin-containing extracts from brown algae inhibited sea urchin larval survival and reduced the appetites of marine herbivores, including sea urchins (Kubanek et al., 2004;Agatsuma, 2008; Shibata et al., 2014). It is hypothesized that its herbivore-repellent effect is due to its ability to bind to digestive enzymes in guts of the herbivores (Barbehenn and Constabel, 2011; Gustavson, 1954;Loomis and Battaile, 1965; Bernays, 1978). However, natural extraction of phlorotannin from seaweed is inefficient given the biomass required due to its low contents (3% (w/w) of dry weight of alginate (Shibata et al., 2002; Arnold and Targett, 2002). Consequently, tannin (TA) is suggested as a phlorotannin alternative because tannin is one of the most abundant and cost-effective polyphenolic compounds obtained from wood bark (Fig. 1a). Both TA and phlorotannin can be precipitated with digestive enzymes from herbivores, so the TA could exhibit herbivore-repellent effects. Recently, green- and cost-effective coatings on various types of target substrates using a Tannin- FeIII complex (TA-FeIII complex) were developed by exploiting a highly stable complex between metal ion/oxide and galloyl residues in tannin and have been applied to variety of biomedical and environmental applications (Zeng and Hwang et al., 2010; Ejima et al., 2013; Oh et al., 2015a). In this study, we report on a TA-Fe III coating used as a coating strategy for marine substrates and for the sustained release of tannin to repel sea urchins from kelp forests. The ability of the TA-FeIII coating to repel sea urchins was evaluated in both a model aquarium and an ocean field experiment.

Section snippets

Chemicals and collection of the sea urchins

Tannin powder from Chinese natural gall nuts, sodium alginate from brown algae and iron chloride(III) were purchased from Sigma-Aldrich (St. Louis, MO, USA). The seawater was collected from the Pohang coast region in Korea (36°9′2.54″N, 129°23′57.18″E), and the filtered seawater was prepared by filtering the collected seawater with a 0.45 μm filter (bottle-top vacuum filters, Corning, NY, USA). Both types of sea water have pH values of 8.1 and 34‰ salinity. The sodium alginate stock solution

Elution rate of TA-FeIII coating

To estimate and control the elution rate of the TA-FeIII eluates from the coating, an elution rate profile of the TA-FeIII coating was obtained using a UV–vis spectrophotometer. The absorbance values of 5, 10, 15, 20, 25, 30, and 50 μM TA-FeIII solution at 280 nm were 0.99, 0.134, 0.166, 0.199, 0.236, 0.284, and 0.471 respectively (Supplementary Material Fig. SM-1a). The absorbance values of the eluates from the TA-FeIII coating were 0.328, 0.333, 0.412, 0.414, 0.409, 0.439 and 0.453,

Conclusion

Given that the need for practical methods to repel sea urchins from kelp forests is increasing, we suggest Tannin -FeIII coating as a repellent agent against sea urchins based on the outstanding repelling effect of this agent against sea urchins as demonstrated using model aquarium and field experiments. Both the model aquarium and field experiments showed that the TA-FeIII coating has a deterrent effect against sea urchins, and we observed that the sea urchins responded to TA-FeIII content in

Credit author statement

Sinyang Kim and Sang Mok Jung conducted the model aquarium experiment, the elution rate measurement and field experiment and they wrote the original manuscript. Sungjune Jung advised and revised the manuscript Dong Soo Hwang and Hyun Woung Shin organized the whole work and revised the manuscript.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

This work was supported by the National Research Foundation of Korea (NRF) grant funded by the Korea government (MSIT) [2016M1A5A1027592].

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