ID Major Adfdrfg Title of Acidification MN Islaaa*, BE Ccccc, and Y Sdddd Graduate School of Science and Technology, Uuuu University, Japan *e-mail: mn_mmmm@uuuu.edu Abstract To test the effects of (4 days under dark condition) were carried out using white coral skeleton (no attachment of living organism), natural rubble (… the control. In the short incubation experiment, addition of bioavailable organic matter further increased carbonate dissolution by enhancing bacterial activity under ambient and high pCO2 condition. These suggest that biological processes play a significant role in determining calcification and dissolution. INTRODUCTION The acidification of the oceans is the ongoing decrease in pH of the oceans, caused by the uptake of anthropogenic CO2 from the atmosphere [1]. Since the beginning of the industrial revolution, about 30–40% of the carbon dioxide approximately 79 million tons per day released in the atmosphere by human activities has been absorbed by the oceans [2-4]. The concentration of carbon dioxide (CO2) in the atmosphere is 396 ppm [5] and increased 2.1 ppm per year during past decade (2003-2012). However, increase in atmospheric CO2 has decreased the world’s ocean pH about 0.001 to 0.002 pH units per year over the past several decades [6]. niferans [13] and also photosynthetic plankton coccolithophorids [14-16] that have shells or plates of calcium carbonate (CaCO3) and leads to dissolution of CaCO3 sediments in reef flats [15]. The acidification of the oceans could affect the dissolution of carbonate skeleton of calcifying organisms as well as coral rubble [17]. Dissolution of carbonate based on the solubility (Ω) of calcite or investigate the importance of biological processes (especially respiration) to the dissolution of calcium carbonate by examining the response of coral rubble and its associated microbial communities with addition of organic matter under elevated pCO2. MATERIALS AND METHODS A. Study area and collection of samples The study area is located in a shallow fringing coral reef at Sesoko Island, Okinawa, Japan between 26°38′ N and 127°51′ E (Fig. 1). Coral rubble coral mucus was collected from Acropora digitifera species using air exposure method [18]. Seawater was collected by using Nalgene bottle and filtered by 0.2 μm isopore membrane cartridge filter before incubation. Fig. 1. Map showing the study area and the location of sample collection (○) at Sesoko Island, Okinawa, Japan (Source: using Google map) B. Preparation of incubation experiment Incubation experiments were carried out in natural illumination (24h short) and dark (4 day’s long) under different level of pCO2 (Ambient, 520, 720 and 1120 (1L) to make final concentration of 10µM. In case of coral mucus, 10% mucus solution was added to the incubation bottles. Temperature and light intensity were monitored during the experiments using in situ sensors (MDS-MkV/T and MDS-MkV/L, Alec electronics). C. Measurement and analysis Measurement of short incubation (natural illumination) experiment was done 24 times per day (1h interval) and 4 times per day (6h interval) for long (Nikon; ECLIPSE/E600), using a UV-filter. Carbonate dissolution rates were analyzed using the alkalinity anomaly technique [19] and saturation state of aragonite (Ωarg) were calculated with the program CO2SYS [20]. RESULTS A. Introducing third sector organizations Natural rubble (NR) are colonized by epilithic and endolithic algal communities and by other heterotrophic organisms as bacteria, foraminifera, nematodes, copepods, etc (Fig. 2, 3, 4). During 4 day’s long incubation experiment under dark condition; the bacterial abundance, net d white skeleton to natural rubble, it is possible to assess that 80% of dissolution was due to the contribution of biological processes (Table 1). Ambient 520 ppm 720 ppm 1 4 1 1 1 4 1 1 5 4 1 1 2 4 1 1 4785 WCSk: White coral skeleton; NR: Natural rubbles with associated epilithic and endolithic communities; Bac. Abundance: Bacterial abundance; Net Res.: Net respiration [ΔCO2 = CO2 final – CO2 initial]; Dis. Rate: Dissolution rate; Sat. State: Saturation state; Mean ± SD Fig. 2. Photograph of natural coral rubble (left) and a transverse section of it (right) showing the endolithic (green band) and epilithic algae [17] B. Addition of bioavailable organic matter Bioavailable organic matter (glucose and coral mucus), was added to the incubation bottles to enhance bacterial growth and their physiological 3bottles, bacterial abundance and dissolution rates increased 5~6 times more than the control (NR) (Table 2). Table 2. Summary result of 24h natural illumination short incubation experiment Bac. Abundance 5 -1 Net Res. Dis. Rate -2 -1 Sat. State -2 -1 [Cells×10 ml ] [mgCm d ] [mmol m d ] [Ωarg] Ambient condition NR 4 High pCO2 (1120 ppm) condition NR 4 NR+G 5 5 5 Fig. 3. Photographs of epilithic microbial communities (a) coccoid green algae; (b) green algae; (c) red calcareous algae; (d) algal colony; (e, f) diatoms; (g) nematode; (h, i) foraminifers; (j) cyanobacteria [17]. 4 4 4 5 5 5 2 5 5 85 5 5 NR: Natural rubbles with associated epilithic and endolithic communities; NR+G: Natural rubbles with addition of organic matter (Glucose); NR+M: Natural rubbles with addition of organic matter (10% Coral mucus); Bac. Abundance: Bacterial abundance; Net Res.: Net respiration; Dis. Rate: Dissolution rate; Sat. state: Saturation state; Mean ± SD C. Carbonate dissolution vs. saturation state Calcium carbonate dissolution rates increased and saturation states (Ωarg) decreased with 33olution rate and saturation state (r=–0.99; p=0.0002)(Fig. 5). Fig. 4. Heterotrophic bacterial communities in coral rubble Table 1. Summary result of 4 day’s long incubation experiment under dark condition Bac. Abundance Net Res. Dis. Rate Sat. [∆CO2 ppm] [mmol m-2d-1] State [Cells×10 ml ] [Ωarg] 3 -1 Fig. 5. Relationship between aragonite saturation state (Ωarg) and carbonate dissolution rates WCSk Ambient 4 4 4 NR 1.12108 ± 0.014 4 4 4 22 4 4 4 22 4 4 4 22 DISCUSSIONS 4 4 4 Dissolution of calcium carbonate of calcifying organisms and their skeletons occurs due to reduction respiration intensified carbonate dissolution. Moreover, when the abundance of bacteria was enhanced with addition of bioavailable organic matter (glucose and coral mucus), the rate of dissolution was further increased (Table 2). Bacterial processes play an important role as demonstrated in the “Bio-Chemical Dissolution Processes (BCDP)” [17] (Fig. 6). Carbonate dissolution occurs when saturation state with respect to carbonate minerals is less than one [9, 10r experiment, dissolution occurred when the saturation state (Ωarg) ranged from 2.87 to 0.88 in coral rubble. 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