Ocean alkalinity enhancement impacts: regrowth of marine microalgae in alkaline mineral concentrations simulating the initial concentrations after ship-based dispersions

Increasing the marine carbon dioxide (CO 2 ) absorption capacity by adding alkaline minerals into the world's oceans is a promising marine carbon dioxide removal (mCDR) approach to increase the ocean's CO 2 storage potential and mitigate ocean acidification. Still, the biological impacts o...

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Bibliographic Details
Published in:Biogeosciences
Main Authors: S. Delacroix, T. J. Nystuen, A. E. D. Tobiesen, A. L. King, E. Höglund
Format: Article in Journal/Newspaper
Language:English
Published: Copernicus Publications 2024
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Online Access:https://doi.org/10.5194/bg-21-3677-2024
https://doaj.org/article/15c1cf837334410982843fba13ee5df1
Description
Summary:Increasing the marine carbon dioxide (CO 2 ) absorption capacity by adding alkaline minerals into the world's oceans is a promising marine carbon dioxide removal (mCDR) approach to increase the ocean's CO 2 storage potential and mitigate ocean acidification. Still, the biological impacts of dispersion of alkaline minerals need to be evaluated prior to its field deployment, especially the impacts of the initial discharge causing local and temporary extreme alkalinity/pH changes. In this study, the toxicity effect on marine microalgae of two commonly used alkaline minerals, calcium hydroxide (Ca(OH) 2 ) and magnesium hydroxide (Mg(OH) 2 ), was determined by adding the same equivalent molar concentration of hydroxyl ions. Cultures of marine green microalgae Tetraselmis suecica were exposed to Ca(OH) 2 or Mg(OH) 2 , in concentrations mimicking the initial high concentrations following a dispersion scenario from a ship. A short-term exposure with high-alkaline mineral concentration called “dispersion phase” was followed by a dilution step and a “regrowth” phase over 6 d. There was no detectable effect of Mg(OH) 2 treatment on algae growth either after the dispersion phase or during the regrowth phase, compared to control treatments. The Ca(OH) 2 treatment resulted in very few living algal cells after the dispersion phase, but a similar growth rate was observed during the regrowth phase as was for the Mg(OH) 2 and control treatments. Standardized whole effluent toxicity (WET) tests were carried out with a range of Mg(OH) 2 concentrations using a sensitive marine diatom, Skeletonema costatum , which confirmed the relatively low toxicity effect of Mg(OH) 2 . Similar biological effects were observed on natural microalgae assemblages from a local seawater source when applying the same Mg(OH) 2 concentration range and exposure time used in the WET tests. The results suggest that Mg(OH) 2 is relatively safe compared to Ca(OH) 2 with respect to marine microalgae.