4.5 Conclusions

This chapter provides an overview how monitoring is addressed in legislation and directives, how guidelines and protocols have been developed to interpret the legislation and how some of the early integrated industrial scale CCS projects have incorporated monitoring plans in their permit applications.

Regulatory regimes in different countries across the world vary. Some countries chose an integrated approach to CCS regulation (i.e. to develop stand-alone legislation), while others decided for a piecemeal approach (i.e. basically amending/updating existing laws and regulations). However, many regulatory regimes took the IPCC Special Report (IPCC; 2005) and IPCC Guidelines (IPCC, 2006) as a starting point. The EU and Australia can be considered the leading players in establishing CCS related regulation frameworks, closely followed by the US and Canada.

A comparison of regulatory documents from different jurisdictions showed, that the objectives for monitoring are similar in terms of tracking the injected fluid in the subsurface and to monitor key risks related to HSE. There is also a common denominator, that monitoring plans should be risk and objectives based, site specific and non-prescriptive in terms of technologies applied. While the EU regulation is entirely focused on emissions reduction objectives, the USA regulation seems more focused on enhanced oil production (EOR) and so called CCUS (carbon capture, use and storage). EU legislation does accept combined EOR and CCS operations, though strictly regulated through the CCS Directive. Moreover, EU legislation requires permanency of stored CO2, while the US (and Canadian) legislation seem to accentuate stronger the utilisation of injected CO2. In all cases long-term liability provisions need further revision and consolidation.

After reviewing the EU and other international/national legislation related to monitoring we can summarize, that regular reporting of the results of monitoring to some kind of competent authority is always requested. In order to verify the content, the performance quality and the relevancy of specific operational procedures and/or corrective measures taken, it will be crucial the reports are inspected by a competent authority. In Annex V of the ETS Directive minimum competency requirements for the verifier are stated. However, the EU CCS Directive does not deal with issues concerning verifier's competency. It may be worth considering the introduction of standards for verification bodies regarding their knowledge, experiences, independency etc. This may result in the introduction of an accreditation procedure for verifiers under the CCS Directive at different levels (national, international).

The permanency of containment of CO2 underground, other than in case of most other subsurface uses, implicates that monitoring data shall be acquired for much longer periods. This issue is related to the handover and specific liability requirements of the state where CCS takes place.

Data retention and ownership of the information from monitoring reports are mentioned in Guidance Document 2 and possible solutions are offered. For example in Europe at present, it is up to the Member States to choose which approach to follow and to establish appropriate regulations concerning the access to and the rights to use the information. It is important to balance between proprietary rights and the transparency for public. At many events (conferences, workshops, panel debates etc.), the dilemma on whether the results of monitoring shall be communicated to a general public arises. Eminent discussion participants (scientists, stakeholders, regulators) are of the opinion that openness and transparency should be a top priority. At least two reasons exist for such conviction: firstly the ability to develop new knowledge through circulation of information and secondly to build public confidence in CCS technology. However, how, who and to what extent to communicate the monitoring results (and other information on CCS in general) remains ambiguous.

Only a limited number of examples of industrial scale integrated projects falling under recent CCS legislation are available. A few of them have been evaluated in this document. Though differences can clearly be identified, all examples follow a similar risk-based approach for defining the monitoring plan.

In all cases wells were identified as potential hazards, either in terms of potential CO2 leakage along the wellbore, or induced brine migration by the elevated pressures in the reservoir. Monitoring tecniques selected depend on the geological setting and on the type of wells. Nevertheless, the monitoring plans do show many similarities.

Probably an issue, that needs to be dealt with in more detail, is on the handling of uncertainties. As stated earlier: "Models should represent the entire uncertainty range, but need to provide sufficient confidence at the same time to carry on the operations."