Dynamic CO 2 and pH levels in coastal, estuarine, and inland waters:Theoretical and observed effects on harmful algal blooms

Rising concentrations of atmospheric CO 2 results in higher equilibrium concentrations of dissolved CO 2 in natural waters, with corresponding increases in hydrogen ion and bicarbonate concentrations and decreases in hydroxyl ion and carbonate concentrations. Superimposed on these climate change eff...

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Bibliographic Details
Published in:Harmful Algae
Main Authors: Raven, John A., Gobler, Christopher S., Hansen, Per Juel
Format: Article in Journal/Newspaper
Language:English
Published: 2020
Subjects:
Online Access:https://discovery.dundee.ac.uk/en/publications/3dba595b-c22b-4d6f-872d-34a889471da8
https://doi.org/10.1016/j.hal.2019.03.012
https://discovery.dundee.ac.uk/ws/files/73738937/1_s2.0_S1568988319300381_main.pdf
http://www.scopus.com/inward/record.url?scp=85063889731&partnerID=8YFLogxK
Description
Summary:Rising concentrations of atmospheric CO 2 results in higher equilibrium concentrations of dissolved CO 2 in natural waters, with corresponding increases in hydrogen ion and bicarbonate concentrations and decreases in hydroxyl ion and carbonate concentrations. Superimposed on these climate change effects is the dynamic nature of carbon cycling in coastal zones, which can lead to seasonal and diel changes in pH and CO 2 concentrations that can exceed changes expected for open ocean ecosystems by the end of the century. Among harmful algae, i.e. some species and/or strains of Cyanobacteria, Dinophyceae, Prymnesiophyceae, Bacillariophyceae, and Ulvophyceae, the occurrence of a CO 2 concentrating mechanisms (CCMs) is the most frequent mechanism of inorganic carbon acquisition in natural waters in equilibrium with the present atmosphere (400 μmol CO 2 mol −1 total gas), with varying phenotypic modification of the CCM. No data on CCMs are available for Raphidophyceae or the brown tide Pelagophyceae. Several HAB species and/or strains respond to increased CO 2 concentrations with increases in growth rate and/or cellular toxin content, however, others are unaffected. Beyond the effects of altered C concentrations and speciation on HABs, changes in pH in natural waters are likely to have profound effects on algal physiology. This review outlines the implications of changes in inorganic cycling for HABs in coastal zones, and reviews the knowns and unknowns with regard to how HABs can be expected to ocean acidification. We further point to the large regions of uncertainty with regard to this evolving field.