Diurnal Changes of pH and Alkalinity on the Coral Reefs of the
Transcription
Diurnal Changes of pH and Alkalinity on the Coral Reefs of the
The Diurnal Changes of Seawater pH and Alkalinity on the Coral Reefs of the Strait of Malacca and the South China Sea Zulfigar Yasin1,2, Nithiyaa Nilamani1, Norhanis Razalli1, Zulfikar3 and Aileen Tan Shau Hwai1 1Marine Science Lab, School of Biological Sciences, Universiti Sains Malaysia, 11800 Minden, Penang, Malaysia. 2Institute of Oceanography and Environment (INOS), Universiti Terengganu Malaysia, 21030 Kuala Terengganu, Terengganu, Malaysia. 3Universitas Malikussaleh, Lhokseumawe, Provinsi Acheh, Indonesia. To investigate the diurnal variation of the seawater pH and alkalinity in shallow water coral reef of Pulau Payar (Strait of Malacca), Pulau Bidong and Pulau Gaya (South China Sea) N Tarutao National Park Pulau Gaya Pulau Bidong Pulau Payar SOUTH CHINA SEA Sumatra 400 km STUDY SITE 3 day period of observation at a shallow water coral reef area Hydrolab DS 5X recorded reading every 15 minute (pH, Temperature, Salinity, Dissolved Oxygen, DO) In-situ measurement & water sample collection Aragonite saturation were determined using the CO2SYS program (Lewis and Wallace, 1998) through in situ AT, pH, salinity, temperature data. Every 3 hours, water sample were collected and measured for the Total Alkalinity (AT) Parameters Unit Measurement Methods Temperature °C Hydrolab DS 5X Salinity ppt Hydrolab DS 5X Hydrolab DS 5X pH Dissolved Oxygen (DO) mg/L Hydrolab DS 5X Total Alkalinity µmol/kg Potentiometric Titration (Dickson et al., 2007) Aragonite Saturation ΩAragonite CO2SYS program (Lewis and Wallace, 1998) • Decreasing surface seawater pH trend from the Strait of Malacca to the South China Sea more basic less basic day night day night day night Payar (SOM) Bidong (SCS) Gaya (SCS) • pH trend fluctuates daily following the diurnal pattern which is regulated by the biological activity such as photosynthesis and respiration day night day night day night Gaya (SCS) Bidong (SCS) Payar (SOM) • • • Total alkalinity (AT) did not show any diurnal trend through out this study. However, the largest range of AT was recorded at Payar with the value of 28.92 μmol/kg. Changes in AT can be attributed to calcification or carbonate dissolution (Murillo et al., 2014) Parameter Symbol Unit Temperature T °C 29.96 ± 0.13 30.05 ± 0.30 30.70 ± 0.52 Salinity S ppt 32.02 ± 0.14 32.60 ± 0.07 32.46 ± 0.08 Total Alkalinity AT μmol kg-1 2140.77 ± 6.29 2161.78 ± 3.08 2160.45 ± 3.41 8.14 ± 0.02 8.01 ± 0.02 7.92 ± 0.01 288.59 ± 13.56 420.11 ± 22.86 531.47 ± 17.00 pH pHT Pulau Payar Pulau Bidong Pulau Gaya ρCO2 in seawater ρCO2 μatm Carbonic acid H2CO3 μmol kg-1 7.36 ± 0.36 10.66 ± 0.63 13.30 ± 0.51 Bicarbonate ion HCO3- μmol kg-1 1523.50 ± 18.55 1654.45 ± 18.86 1718.85 ± 13.03 Carbonate ion CO32- μmol kg-1 250.49 ± 6.65 206.22 ± 8.25 179.82 ± 5.48 Hydrogen ion H+ μmol kg-1 7.32 x 10-3 ± 0.00 9.83 x 10-3 ± 0.00 1.19 x 10-2 ± 0.00 Calcite saturation Ωcalc 6.25 ± 0.17 5.12 ± 0.21 4.48 ± 0.14 Aragonite saturation Ωarag 4.16 ± 0.11 3.41 ± 0.14 2.99 ± 0.10 Lower pH value and higher total alkalinity than Payar Lower salinity and total alkalinity but higher pH Parameter Symbol Unit Temperature T °C 29.96 ± 0.13 30.05 ± 0.30 30.70 ± 0.52 Salinity S ppt 32.02 ± 0.14 32.60 ± 0.07 32.46 ± 0.08 Total Alkalinity AT μmol kg-1 2140.77 ± 6.29 2161.78 ± 3.08 2160.45 ± 3.41 8.14 ± 0.02 8.01 ± 0.02 7.92 ± 0.01 288.59 ± 13.56 420.11 ± 22.86 531.47 ± 17.00 pH pHT Pulau Payar Pulau Bidong Pulau Gaya ρCO2 in seawater ρCO2 μatm Carbonic acid H2CO3 μmol kg-1 7.36 ± 0.36 10.66 ± 0.63 13.30 ± 0.51 Bicarbonate ion HCO3- μmol kg-1 1523.50 ± 18.55 1654.45 ± 18.86 1718.85 ± 13.03 Carbonate ion CO32- μmol kg-1 250.49 ± 6.65 206.22 ± 8.25 179.82 ± 5.48 Hydrogen ion H+ μmol kg-1 7.32 x 10-3 ± 0.00 9.83 x 10-3 ± 0.00 1.19 x 10-2 ± 0.00 Calcite saturation Ωcalc 6.25 ± 0.17 5.12 ± 0.21 4.48 ± 0.14 Aragonite saturation Ωarag 4.16 ± 0.11 3.41 ± 0.14 2.99 ± 0.10 More carbonate ion available in the seawater Lower carbonate ion concentration GBP G – Gaya B – Bidong P – Payar Pulau Bidong and Pulau Gaya (South China Sea) Higher AT were recorded at these sites, 2161.78 μmol kg-1 and 2160.45 μmol kg-1 respectively. The pH at both sites in the South China Sea are lower than Paya (St of Malacca) as denoted by the higher H+ concentration in the seawater. Aragonite saturation in the seawater at both sites were recorded at adequate (3.41) and marginal (2.99) level respectively. Pulau Payar (Strait of Malacca) Lower AT (2140.77 μmol kg-1) means the capacity of the seawater buffer system to neutralize acidic pollution is reduced. At present, the seawater carbonate system is maintained because of the pH value (pH 8.14). Only a small amount of acidic pollution is needed to disrupt the carbonate system equilibrium. Optimal aragonite saturation state in Payar contributes to the high coral calcification rate in the area. Parameter Symbol Unit Temperature T °C Total Alkalinity AT μmol kg-1 pH pHT Pulau Payar Pulau Bidong Pulau Gaya 29.96 ± 0.13 30.05 ± 0.30 30.70 ± 0.52 2140.77 ± 6.29 2161.78 ± 3.08 2160.45 ± 3.41 8.14 ± 0.02 8.01 ± 0.02 7.92 ± 0.01 ρCO2 in seawater ρCO2 μatm 288.59 ± 13.56 420.11 ± 22.86 531.47 ± 17.00 Bicarbonate ion HCO3- μmol kg-1 1523.50 ± 18.55 1654.45 ± 18.86 1718.85 ± 13.03 Carbonate ion CO32- μmol kg-1 250.49 ± 6.65 206.22 ± 8.25 179.82 ± 5.48 Calcite saturation Ωcalc 6.25 ± 0.17 5.12 ± 0.21 4.48 ± 0.14 Aragonite saturation Ωarag 4.16 ± 0.11 (Optimal) 3.41 ± 0.14 (Adequate) 2.99 ± 0.10 (Marginal) Source: Reefs at Risk Revisited (2011) Calcification Rate of Porites sp. (g cm-2 yr-1) Strait of Malacca SW of South China Sea SE of South China Sea 2.1 (Payar) Tanzil et al., 2013 2.1 (Redang) Tanzil et al., 2013 0.7 (Spratly Islands) Ruixia et al., 2012 Studies on calcification rates and reef integrity in the region taking into consideration local stressors Develop and agree on a common methodology for the monitoring of ocean acidification on coral reefs Increase the number and spread of long term monitoring sites and separation between OA and other anthropogenic effects on reefs Develop baseline carbonate chemistry information and data sharing for the Southeast Asia region and selected Class III sites. Consider the depth of certain reefs and the effect OA on these and associated biota Integrate the findings of this group with the other physical and chemical approaches of ocean acificication studies and beyond. Relate to socio-economics of reef use and especially to fisheries. Studies on calcification rates and reef integrity in the region Increase the number and spread of long term monitoring sites and separation between OA and other anthropogenic effects on reefs Develop and agree on a common methodology for the monitoring of ocean acidification on coral reefs Develop baseline carbonate chemistry information and data sharing for the Southeast Asia region and selected Class III sites. Consider the depth of certain reefs and the effect OA on these and associated biota Integrate the findings of this group with the other physical and chemical approaches of ocean acificication studies and beyond. Relate to socio-economics of reef use and especially to fisheries. Pulau Payar St. A St. B St. C St. D Caulastrea Latitude Genera Montastrea Acropora Pectinia Symphyllia Diploastrea D C B A Favia Favites Goniastrea Porites Total 4 8 7 7 Longitude Template of study is adopted for reef monitoring studies by the Malaysia’s Marine Park in collaboration with Universiti Malaysia Terengganu and Universiti Sains Malaysia. Current location of monitoring stations are in the: • Straits of Malacca (Sabang and Langkawi) • Eastern portion of the South China Sea (Bidong, Terengganu) • Western portion of the South China Sea (Pulau Gaya, Kota Kinabalu We wish to thank the following institutions for their generous suport: Ministry of Science and Technology of Malaysia (MOSTI) Ministry of Natural Resources and Environment (NRE) The Marine Park Department of Malaysia Universiti Sains Malaysia (USM) Universiti Malaysia Terengganu (UMT) Thank you for your kind attention [email protected]