“…Both nesquehonite and dypingite are readily formed during reaction of Mg-rich minerals with CO 2 at ambient temperatures, with nesquehonite tending to form at greater than atmospheric pCO 2 or evaporative conditions (Königsberger et al, 1999;Power et al, 2007;Xiong and Lord, 2008;Zhao et al, 2010;Schaef et al, 2011;Harrison et al, 2013a), and dypingite favored under atmospheric pCO 2 (~400 ppm) and microbially-mediated conditions (Power et al, 2007;Wilson et al, 2010;Mavromatis et al, 2012;Shirokova et al, 2013;Harrison et al, 2013a;McCutcheon et al, 2016). In addition to their natural occurrence and use for CO 2 storage, hydrated Mg-carbonates have prompted interest due to their potential formation in engineered Mg(OH) 2 /MgO barriers for nuclear waste storage (Xiong and Lord, 2008;Xiong, 2011), and the precipitation of nesquehonite from MgCl 2 brines has been investigated as a way to exploit Mg resources from salt lakes (Dong et al, 2008;Wang et al, 2008;Cheng et al, 2009;Cheng and Li, 2009), and as a precursor for high purity MgO production (Cheng et al, 2009;Wang and Li, 2012). This broad interest in nesquehonite has inspired a number of studies regarding its thermal stability (Lanas and Alvarez, 2004;Hales et al, 2008;Vágvölgyi et al, 2008;Ballirano et al, 2010;Jauffret et al, 2015;Morgan et al, 2015), nucleation kinetics (Cheng and Li, 2010;Zhao et al, 2013), its tendency for solid-solution with transition metals (Hamilton et al, 2016), and the impacts of temperature, saturation state, and fluid composition on nucleation and crystal morphology and size (Zhang et al, 2006;Wang et al, 2008;Cheng et al, 2009;…”