ince the industrial revolution, the global ocean has absorbed approximately 30% of the anthropogenic CO 2 emissions from the atmosphere, lowering the average surface ocean water pH by 0.1 units and aragonite carbonate mineral saturation state (Ω arag ) by 0.5 units. This process, known as ocean acidification 1,2 , is harmful to some marine organisms and ecosystems 3 . In coastal waters, acidification is enhanced by eutrophication and the subsequent hypoxia and anoxia via the accumulation of CO 2 and acids below the pycnocline 4,5 . Calcium carbonate (CaCO 3 ) mineral dissolution can increase the total alkalinity (TA) of water, and is proposed as a buffer to neutralize anthropogenic CO 2 uptake 6,7 . Recent studies have shown that CaCO 3 dissolution can offset a notable proportion of the metabolic CO 2 and increase survivorship of juvenile bivalves, thus providing a substantial negative feedback to coastal acidification 8,9 .However, very few studies have linked CaCO 3 dissolution to the timing and location of its formation in coastal waters 10,11 as a corollary to the ocean's carbonate counter pump 11 . These dynamic links are essential to understand given their capacity to mediate aquatic pH and atmospheric CO 2 concentrations 8,12 . In coastal waters, CaCO 3 can be formed via abiotic precipitation or biotic production, which are usually associated with coral reefs, calcareous algae 13 , molluscs 14 , bacteria 15 , fish 16 and aquatic plants 17 . Recently, seagrass meadows have been shown to be major sites for CaCO 3 accumulation and storage in high-salinity waters in equatorial and subtropical regions 18 . In addition to calcification from the seagrass-calcifying algae, infauna and epibiont community, the seagrass Thalassia testudinum