3.4.1 Effects of leakage of CO2 into the groundwater

The leakage of CO2 or the displacement of brine into a groundwater aquifer produces significant changes in groundwater chemistry and quality and may also cause physical impacts by interfering with groundwater extraction procedures when a large plume of gaseous CO2 is involved (Esposito and Benson, 2011). The contamination of groundwater with CO2 would lead to the formation of carbonic acid, which causes a decrease of pH, enabling dissolution of carbonate minerals and mobilisation of trace chemicals.

For the Zero Emission Research and Technology (ZERT) experiment in Montana, USA, food grade CO2 was injected over a period of one month during which an intensive monitoring program, including water sampling, was performed. This experiment revealed significant changes in chemical parameters measured at the site, including a relatively rapid decrease of pH (7.0 to 5.6), increase of alkalinity (400 to 1,330 mg/l as bicarbonate, HCO3-), and electrical conductance (600 to 1,800 lS/cm) and an increase of natural trace chemicals (lead, arsenic, benzene) content following CO2 injection (Kharaka et al., 2010). The increased levels of contaminants in the groundwater could pose a serious threat to human health if the groundwater aquifer is used as water supply or the reservoir is connected with water supplies.

Modelling CO2 intrusion into groundwater aquifers revealed mobilisation of lead and arsenic as a result of the contamination, while for aquifers with low velocity, the impact of CO2 intrusion can be more significant but is also more localised (Zheng et al., 2009).

Another aspect of CO2 leakage into the groundwater is the interactions of co-injected/co-transported gases with the mineral matrix and the subsurface water. According to the modelling work of Harvey et al. (2012), there is a significant difference between the geochemical impact of a mixed gas (99.4% CO2, 0.1% CO, 0.1% NOx, 0.3% SOx and 0.1% CH4) and a CO2-only stream (which cannot be obtained with the current capture technologies) as the co-injected/co-transported gases could potentially influence aqueous speciation and mobility of redox-sensitive elements such as Iron and Arsenic. Co-transported NOx or SOx into potable groundwater or soil pore water could contribute to additional lowering of the pH (up to 1 unit) that could lead to enhanced release of trace metals and formation of carcinogenic nitroso compounds (from Nitrogen dioxide NO2 and organic matter) (Harvey et al., 2012). The same authors also proposed the conceptual framework for assessing geochemical impact of CO2 on near surface environments, presented in the Fig. 3-2.

O. Fig. 3-2

Fig. 3-2: A conceptual framework for assessing geochemical impact of CO2 on near surface environments (after Harvey et al., 2012)