Quantifying and monitoring potential ecosystem impacts of geological carbon storage Fact Sheet 13 Biogeochemical impacts of leaking CO2 What happens when CO2 reacts with sea water? When CO2 dissolves into sea water it reacts to form a weak acid (carbonic acid - H2CO3) that readily releases hydrogen ions (H+), contributing to increased acidity (= pH decrease) and an increased concentration of bicarbonate (HCO3-) ions (figure 1). Calcium carbonate-rich (CaCO3) sediment composed of shells and skeletal material from marine animals (e.g. mussels, snails, brittle stars, sea urchins etc.) may start to dissolve in order to ‘compensate’ for the drop in pH caused by the injected CO2 gas (figure 1). This buffering process limits acidification but potentially at the expense of the shells and skeletal structures in marine animals. Figure 1. How injected CO2 gas dissolves and reacts with water within sediments and above the sea floor. Biogeochemical impacts in the sediment During the QICS controlled CO2 release experiment in Ardmucknish Bay (Scotland), 4.2 tonnes of CO2 gas was injected at a depth of 12 metres below the sea floor over 37 days. Data recorded by CO2 sensors and analysis of sediment cores collected by divers revealed that the injected CO2 gas release had an impact on the acidity (pH), dissolved CO2 and buffering capacity of the sea bed sediment (figures 2 & 3). Figure 2. Variation in geochemical parameters in the sediment during the QICS experiment. Biogeochemical impacts of the injected CO2 gas were highly localised and only observed in shallow sea bed sediments over the centre of the injection after five weeks of gas release. At this stage the dissolved CO2 concentrations and the sediment buffering capacity (i.e. total alkalinity) increased by more than 10 times compared to background values. pH initially dropped with increasing CO2 but then increased to near baseline levels as the buffering increased, (figure 2). An increase in the concentration of dissolved metals, such as calcium, iron, manganese and some trace metals, were also observed during the release period. All of these changes persisted for at least a week after the gas release was stopped, however three weeks after CO2 injection ceased these parameters returned to their normal values (figure 2). www.qics.co.uk Quantifying and monitoring potential ecosystem impacts of geological carbon storage Figure 3. Showing from left to right: sea floor CO2 sensor; diver collecting sea water samples; two sea bed CO2 sensors near a stream of CO2 bubbles; diver collecting sediment core samples. Biogeochemical impacts & fluxes in the water column Elevated CO2 concentrations and lowered pH were measured by CO2 sensors in the sea water near the CO2 bubble streams (Figure 4). The extent of the high CO2/low pH sea water plume was confined to an area approximately 25 metres in diameter above the gas injection point and closely corresponded with the visual observations of CO2 bubbles. The plume of sea water with high CO2/low pH reached the sea-surface (approximately 12 metres above the sea bed) during low tide. The gaseous CO2 flux into the water column was measured at ≤15% of the injected volume of CO2, with 85% of the gas presumed to remain trapped within the sediments, either dissolved in the sediment water or trapped as either gas or in mineral form (figure 1). However modelling estimates suggest that some dissolved CO2 escaped the sediments, with only ~50% of the CO2 retained in the sediments. Figure 4. A plot of the CO2 content of sea water (partial pressure, pCO2) recorded by a sensor towed 1 metre above the sea floor, across the centre of the release and the area unaffected by the release. Inset: bathymetry survey data shows peaks of gas ‘flares’ that correspond to the plot of elevated CO2 content. Summary points • The biogeochemical impacts of the injected CO2 on water within sea bed sediment and sea water overlying the sea floor were clearly distinguished. • Only the area above the release point was effected and the biogeochemistry of the sea bed sediment and sea water returned to normal values within weeks of switching off the CO2 gas. • Shells of calcium carbonate (CaCO3) within the sea bed sediment dissolved to compensate for acidification caused by the injected CO2. • Only 15% of injected CO2 escaped (as gas bubbles) from the sea bed into the overlying sea water with some rising to the sea surface to enter the atmosphere. • A significant proportion of the injected CO2, was retained within the sea bed sediment above the release points in dissolved, gaseous or mineral form. • The chemical observations indicate that leakage will be readily detectable by chemical sensors in the water column, but for leaks of this magnitude, only within a few metres of the release point. QICS Project Office www.bgs.ac.uk/qics/ www.qics.co.uk Plymouth Marine Laboratory, UK Project Leader: Jerry Blackford QICS [email protected] led by Plymouth Marine Laboraory in the UK, contact Jerry Blackford | [email protected] further information Contact:
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