Abstract

AEI Aquaculture Environment Interactions Contact the journal Facebook Twitter RSS Mailing List Subscribe to our mailing list via Mailchimp HomeLatest VolumeAbout the JournalEditorsTheme Sections AEI 11:671-684 (2019) - DOI: https://doi.org/10.3354/aei00340 Using macroalgal bioindicators to map nutrient plumes from fish farms and other sources at a bay-wide scale L. M. Howarth1,*, R. Filgueira1, D. Jiang1, H. Koepke1, M. K. Frame1, C. Buchwald1, S. Finnis1, T. Chopin2, S. D. Costanzo3, J. Grant1 1Oceanography, Dalhousie University, 1355 Oxford Street, B3H 4R2 Halifax, Nova Scotia, Canada 2Seaweed and Integrated Multi-Trophic Aquaculture Research Laboratory, University of New Brunswick, E2L 4L5 Saint John, New Brunswick, Canada 3Integration and Application Network, University of Maryland Center for Environmental Science, Cambridge, MD 21613, USA *Corresponding author: leigh.howarth@dal.ca ABSTRACT: Human activities can elevate coastal levels of dissolved inorganic nitrogen (DIN). As macroalgae readily absorb and accumulate DIN, the elemental (total N and C:N ratio) composition of their tissues is less affected by temporal fluctuations compared to more direct measures of DIN concentration. Additionally, their isotopic (δ15N) composition can reflect that of the source, which could potentially be used to identify between multiple effluent sources. To investigate whether macroalgal ‘bioindicators’ could map and distinguish between multiple effluents, 2 species of macroalgae (Chondrus crispus and Palmaria palmata) were deployed in a bay containing a salmon farm and sewage treatment facility. Both species exhibited high total N and low C:N ratio near the salmon farm and sewage facility. However, the elemental composition of C. crispus was influenced over a greater distance than that of P. palmata. Differences were also observed between their isotopic composition, as C. crispus indicated that the salmon farm and sewage facility had distinct δ15N signatures, whereas values of δ15N in P. palmata had not changed after 10 d incubation in the field. Interestingly, the distinct isotopic signals observed in C. crispus were likely a result of higher DIN concentrations at the salmon farm, which likely caused macroalgae to fractionate and form biomass lighter in δ15N. Overall, this study suggests that macroalgal bioindicators can monitor and identify between multiple effluent sources, which could provide a useful tool for coastal management. However, some species of macroalgae may make more effective bioindicators than others, and the mechanisms underlying their fractionation require further investigation. KEY WORDS: Aquaculture · δ15N · Isotope · Macroalgae · Nitrogen · Salmon · Sewage · Wastewater Full text in pdf format Supplementary material PreviousNextCite this article as: Howarth LM, Filgueira R, Jiang D, Koepke H and others (2019) Using macroalgal bioindicators to map nutrient plumes from fish farms and other sources at a bay-wide scale. Aquacult Environ Interact 11:671-684. https://doi.org/10.3354/aei00340 Export citation RSS - Facebook - Tweet - linkedIn Cited by Published in AEI Vol. 11. Online publication date: December 19, 2019 Print ISSN: 1869-215X; Online ISSN: 1869-7534 Copyright © 2019 Inter-Research.

Highlights

  • Human activities can elevate nutrient levels in coastal environments (Nixon 1995, Smith 2003, Eddy 2005)

  • Our results suggest that the dissolved inorganic nitrogen (DIN) released from the salmon farm and sewage treatment facility had increased the growth of macroalgal bioindicators

  • This study investigated whether macroalgal bioindicators could be used to map and identify between multiple effluent sources

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Summary

Introduction

Human activities can elevate nutrient levels in coastal environments (Nixon 1995, Smith 2003, Eddy 2005). Particulate wastes derive from faeces and uneaten feed, and represent between 13 and 32% of all the N released from fish farms (Islam 2005, Holmer et al 2007, Sanderson et al 2008, Callier et al 2013). These particulate wastes quickly settle onto the seafloor and rarely disperse more than a few hundred metres (Brager et al 2015, Price et al 2015, Bannister et al 2016, Filgueira et al 2017). This dissolved fraction makes up the majority of fish farm wastes, less is known about its dispersal and persistence within the marine environment (Price et al 2015, Jansen et al 2018)

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