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Coral growth and bioerosion as functions of temperature anomaly in west (W) and east (E), 7 m and 20 m depth. Coral growth rate of Porites lutea nubbins at all study sites (n = 20, df = 1, F-value = 4.4, r 2 = 0.46, p = 0.039) along the Similan island chain after 12 months exposure (February 2007 to February 2008; see Fig. 4) (A), and bioerosion (calculated mass change in calcium carbonate (CaCO 3 ) corrected for accretion due to fouling organisms) on CaCO 3 blocks at the central Similan island Ko Miang (see Fig. 1) after 12 months (grey depiction; February 2007 to February 2008; n = 4, degrees of freedom = 1, F-value = 14.4, r 2 = 0.30, p,0.001) and 21 months exposure normalized to 1 year (February 2007 to November 2008; n = 4, degrees of freedom = 1, F-value = 17.9, r 2 = 0.58, p,0.001) (see Fig. 5; ,0, bioerosion) (B) as functions (GLM) of the cumulative negative temperature anomaly (calculated as uC d) of the respective time period. All values are plotted as mean 6 SE. doi:10.1371/journal.pone.0073236.g007

Coral growth and bioerosion as functions of temperature anomaly in west (W) and east (E), 7 m and 20 m depth. Coral growth rate of Porites lutea nubbins at all study sites (n = 20, df = 1, F-value = 4.4, r 2 = 0.46, p = 0.039) along the Similan island chain after 12 months exposure (February 2007 to February 2008; see Fig. 4) (A), and bioerosion (calculated mass change in calcium carbonate (CaCO 3 ) corrected for accretion due to fouling organisms) on CaCO 3 blocks at the central Similan island Ko Miang (see Fig. 1) after 12 months (grey depiction; February 2007 to February 2008; n = 4, degrees of freedom = 1, F-value = 14.4, r 2 = 0.30, p,0.001) and 21 months exposure normalized to 1 year (February 2007 to November 2008; n = 4, degrees of freedom = 1, F-value = 17.9, r 2 = 0.58, p,0.001) (see Fig. 5; ,0, bioerosion) (B) as functions (GLM) of the cumulative negative temperature anomaly (calculated as uC d) of the respective time period. All values are plotted as mean 6 SE. doi:10.1371/journal.pone.0073236.g007

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The Similan Islands (Thailand) in the Andaman Sea are exposed to large amplitude internal waves (LAIW), as evidenced by i.a. abrupt fluctuations in temperature of up to 10°C at supertidal frequencies. Although LAIW have been shown to affect coral composition and framework development in shallow waters, the role of LAIW on coral growth is so far unk...

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... calculated with coral growth or bioerosion as dependent variable and temperature anomalies calculated for the respective exposure periods as independent variables. The results show that both coral growth (r 2 = 0.46, p = 0.039) and bioerosion after 12 (r 2 = 0.30, p,0.001) and 21 months exposure (r 2 = 0.59, p,0.001) are inversely related to LAIW (Fig. ...
Context 2
... growth, compared to the monsoon affected (W 7 m) and sheltered (E 7 m, E 20 m) sites. This may be due to the combined effect of unfavourable environmental conditions, notably lower temperature, light and pH in W 20 m compared to the other sites [31]. The GLM analysis shows that coral growth rates correlated well with temperature anomaly (Fig. 7), under- scoring the potential role of LAIW in suppressing coral growth. The growth rates in W 7 m are important in assessing the relative importance of monsoon and LAIW for reef growth [32] by showing that monsoon exposure did not limit skeletal growth. It is likely that the high water motion here enhanced metabolic rates and ...
Context 3
... was highest in E and lowest in W (Fig. 6) and showed an inverse relationship with temperature anomaly (Fig. 7) refuting our hypothesis of LAIW-(i.e. nutrient-) enhanced bioerosion. However, bioerosion has also been shown to be related to coral cover [2,14], in line with the observation of higher reef development in E [31,32]. This is because higher coral cover provides more habitats for internal and external bioeroders, notably living space for ...

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... This region is a good demonstration, however, that favorable conditions imposed by IGWs are not necessarily consistent yearround, because factors such as thermocline depth, tidal range, and other oceanic and atmospheric forcings also determine if and when thermal conditions are present at depths beneficial to reefs. IGWs can have detrimental effects on reefs as well, such as depressing coral growth (Schmidt and Richter, 2013) or limiting the maximum depth of reef development (Wyatt et al., 2020). The Galaṕagos and eastern Pacific locations, for example, experience a deepened thermocline during El Niño events so that IGW-induced cooling would be diminished. ...
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... kg CaCO 3 m −2 yr −1 , 30 months deployment). This is a moderate rate compared to the larger net erosion observed in the GBR, French Polynesia, and Thailand (−4 or −8 kg CaCO 3 m −2 yr −1 ) (Osorno et al., 2005;Pari et al., 1998;Schmidt and Richter, 2013;Tribollet and Golubic, 2005). ...
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... Compared to the sheltered site, the exposed site features higher temperature fluctuations (up to 6-9 °C) and pH variability (by up to 0.6 units) that last for 15-30 min, higher nutrient and lower oxygen levels ( Schmidt et al., 2012;Wall et al., 2012Wall et al., , 2014). As a result, LAIW-exposed corals show higher nutritional status ( Roder et al., 2010Roder et al., , 2011), higher feeding capacity and higher photosynthetic efficiency ( Pacherres et al., 2013) but lower growth ( Schmidt and Richter, 2013). LAIW and monsoon impact are disturbances that depress framework development ( Schmidt et al., 2012). ...
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