5.2.1 Regulatory regime for site remediation in Europe

The EU CCS Directive (2009) and its Guidance Documents 1 and 2 (EC, 2011a, b) represent the principal regulatory regime for all EU Member States in relation to the geological storage of carbon dioxide, although additional regional and local regulations may exist in the Member States.

In terms of reasons for site remediation, the CCS Directive defines:

  • Leakage: any release of CO2 from the storage complex (storage site and surrounding geological domain, which can have an effect on overall storage integrity and security; that is, secondary storage containments).
  • Significant irregularity: any irregularity in the injection or storage operations or in the condition of the storage complex itself, which implies the risk of a leakage or risk to the environment or human health.

The EU CCS Directive requires that a corrective measures plan is prepared by the operator and submitted as part of the storage permit application, which should be "ready to use" (in the sense described by Kuuskraa and Godec, 2007) immediately in case of leakage or significant irregularities. Article 16 of the CCS Directive describes the measures that should be taken in case of leakage or significant irregularities and states that Member States shall ensure:

  • That in the event of leakages or significant irregularities, the operator immediately notifies the competent authority, and takes the necessary corrective measures, including measures related to the protection of human health. In cases of leakages and significant irregularities which imply the risk of leakage, the operator shall also notify the competent authority pursuant to the EU ETS Directive (2003).
  • The corrective measures referred above shall be taken as a minimum on the basis of a corrective measures plan submitted to and approved by the competent authority in the application permit.
  • The competent authority may at any time require the operator to take the necessary corrective measures, as well as measures related to the protection of human health. These may be additional to or different from those laid out in the corrective measures plan. The competent authority may also at any time take corrective measures itself.
  • If the operator fails to take the necessary corrective measures, these measures shall be taken by the competent authority, which shall recover the costs from the operator including by drawing on the financial security pursuant to Article19 of the EU CCS Directive.

Corrective measures are actions, measures or activities taken to correct significant irregularities or to close leakages in order to prevent or stop the release of CO2 from the storage complex. Intended to ensure the safety and effectiveness of geological storage, corrective measures are part of the overall risk management process. They ensure the safety of geological storage and manage the risks from leakage during the project life cycle. Corrective measures, as mentioned in the Guidance Document 2 (EC, 2011b), should be:

  • Risk based; linked to identified risks from site and complex characterization (and risk assessment) and subject to the limitations of available technologies;
  • Specific to the storage site and complex;
  • Suitable for use to address leakage or significant irregularities from identified leakage pathways and specific leakage mechanisms out of the storage complex and any leakage to the surface;
  • Closely linked to monitoring plans and monitoring, which should provide triggers for use of corrective measures by identification of leakage or irregularities;
  • Used when there is any leakage or significant irregularities.

Monitoring and corrective measures are closely interlinked and the plans and activities should be developed by the operator in a wholesome manner along with the risk assessment. The competent authority should seek to ensure close integration between these measures.

The deployment of corrective measures is required in the event of leakages or significant irregularities, and would usually be detected by monitoring results or inspections. In addition monitoring is used to assess the effectiveness of corrective measures. Additional monitoring activities may be required in event of any leakage or significant irregularities.

Corrective measures may be used at any stage in the life cycle after storage permit award and are expected to be used mostly during the operations (injection) phase and post-closure pre-transfer phase. After transfer of responsibility, corrective measures may still be required, although the likelihood is reduced from then on as the CO2 plume reaches stability.

Under normal operating conditions, in the event of leakages or significant irregularities, the operator has to immediately notify the competent authority both under the EU CCS Directive (2009) and the EU ETS Directive (2003) and take the necessary corrective measures, including measures related to the protection of human health. Measures approved in the corrective measures plan shall be taken as a minimum.

Initial plans will be based on the risks identified for the storage complex, with predicted pathways and scenarios for potential leakage based on site characterization and modelling. The types of risk and pathways would likely be similar to generic types of pathways that are described in Guidance Document 1 (EC, 2011a), primarily either geological pathways (e.g. faults, fractures or caprock absence), manmade pathways (i.e. well bores or old mine workings) or the other types of risk (e.g. groundwater contamination, displaced oil and gas, subsidence). The general locations of many potential pathways can be predicted ahead of any leakage situation, e.g. the location of a major fault or a wellbore. However, some potential leakage pathways may not be detectable (e.g. sandstone intrusions) with current technologies at the time of initial risk assessment and corrective measure plans or their locations may be uncertain. If these emerge subsequently, site characterisation, risk assessment, monitoring and corrective measures plans will need to be updated as necessary.

The operator and competent authority should consider that the actual and specific location of any significant irregularity or leakage will usually not be known before it is detected, nor will the actual pathway between the leak and the surface if the flow is not direct (which may be the case as a leak may involve a complex three dimensional problem combining the geology and well pathways). The corrective measures will ultimately need to be specific to the actual leakage or significant irregularity, taking into account the precise location and nature of the leakage or irregularity, and the specific situation and circumstances in which the leak occurred. Flexibility is required to update and change the plan according to the specific situation.

Early warning and early intervention in the detection of significant irregularities will urge to take action through corrective measures to prevent the situation getting worse, and reduce the risk of actual leakage from the storage complex. In the event of a leakage or significant irregularity the operator must immediately notify the competent authority and take the necessary corrective measures, including measures related to the protection of human health. The competent authority needs to ensure the immediate implementation of correctives measures as a minimum on the basis of the presented corrective measures plan. Handling and implementing corrective measures in the event of actual leakage to surface will require rapid and effective interaction between the competent authority and operator. It will require strong technical expertise in drilling, well engineering and geosciences. Specialist consultants would often be involved in comparable situations in the oil and gas industry. competent authorities will need to know what expertise exists within their organizations and where and when to draw on external experts.

Corrective measures can be applied to two major types of pathways: (1) to the natural, geological system and (2) to the engineered, wellbore system. While technically it is feasible to implement corrective measures and repairs, in general, their effectiveness and potential to restore the geological system is considered limited. In principle, the well can be accessed, allowing tools to be run or operations to be performed in order to repair leakages or irregularities of the wellbore and its immediate surroundings. Wells actually are the only direct connection to the subsurface. Flaws in the geological system can typically be corrected only when wells are penetrating the affected zone. Nevertheless, geological anomalies may often reflect three-dimensional problems, significantly extending the vertical and/or lateral directions, rather than giving a localized problem. This reduces the number of options to repair the issue. Corrective measures involving early interventions and modifications to injection operations will usually be beneficial and can provide effective risk management in some circumstances. The Guidance Document 2 (EC, 2011b) and the Aspen Report (Arts et al., 2009) summarise some of the corrective measures methods both for geological system and wells.

Managing injection rates, locations and pressures can be used to manage some of the risks relating to geological leakage pathways and risks. However, many of the other technologies for managing issues related to geological pathways are more novel and also uncertain. Technique effectiveness involving new wells that intersect with plumes or pathways will depend on being able to identify the target area, which may be difficult in a three dimensional space. Other techniques with extraction of either CO2 or water are technically plausible but handling the produced fluids and undertaken costs will need to be evaluated on a case by case basis. We should take into consideration that:

  • Any corrective measures will be highly specific and need to take account the nature, flux and location of the leakage or irregularity (in three dimensions), which may be poorly understood especially for geological pathways.
  • Gathering further data through monitoring and re-evaluation of site characterization and modelling is essential.
  • Corrective measures for dealing with leakage or significant irregularities from wells are generally considered feasible using techniques and practices from the oil and gas industry or gas storage.
  • Managing injection rates, locations and pressures can be used to manage some of the risks relating to geological leakage pathways and risks.
  • Other approaches involving extraction of CO2 or water are possible but the fluids produced will need to be handled and the costs may be high.
  • The costs of any corrective measures will be highly uncertain and specific to the leakage or irregularity being addressed.

CAs should be aware that the status of the technologies that may be used for corrective measure is highly variable. Virtually none of the technologies have yet been used in CO2 storage applications or environments.

The EU CCS Directive requires that the corrective measures plan be based on the risk assessment. For risks identified during the risk assessment, corrective measures have to be developed and described in the corrective measures plan. Currently, such measures are available only for certain kinds of risks. In some cases, only very generic measures like reducing reservoir pressure or aborting injection are currently proposed.

The corrective measures plan has to be handed in as part of the storage permit application. Detailed corrective measures have to be developed before injection has started. It can be assumed that, in case a risk materializes, it has to be assessed, whether the foreseen corrective measure is suitable, or whether changes to the measures are needed. Over the lifetime of a storage site new corrective measures might emerge or the approach in measures might change. Furthermore, with increased experience about the storage site, risks might be considered irrelevant or new risks might. It thus seems advisable to regularly update the corrective measures plan. This could be in line with the timeframe for regular updating of the monitoring plan.

The Guidance Document 2 (EC, 2011b) and the Aspen Report (Arts et al., 2009) propose a possible format for the corrective measures plan aiming to enhance transparency and comparability as well as exchange of information with regards to corrective measures plan. It consists of two parts. In the first section (Tab. 5-1) an overview is given on the corrective measures to be taken for the risks identified. Threshold values or qualitative circumstances are stated, which will trigger the implementation of a corrective measure. Furthermore, the monitoring methods used to monitor the effectiveness of a corrective measure are named together with the number of the method from the monitoring plan (used for easier identification of methods throughout the plan). In the second part of the plan (Tab. 5-2), each corrective measure is described in detail with regards to the timeframe needed for implementation and the detailed activities to be carried out. Furthermore, a rationale is to be delivered, why the corrective measure is appropriate for the risk it is related to.

Tab. 5-1: Corrective measures plan section 1 - Overview of risks and measures (Guidance Document 2, EC, 2011b).

Risk the measure is related to

Irregularity this measures is related to

Corrective measure

No. of corrective measure

Monitoring method (s)

No. of monitoring method

Comment:

Please state the risk(s) as identified in the risk assessment

Comment:

Please state the threshold values or qualitative conditions which will trigger this corrective measure

Comment:

Please state name and number of the monitoring method(s) used to monitor the effectiveness of the corrective measure, as stated in Table 1

Measure A

No. 1

Method D

No. 4

Measure B

No. 2

Tab. 5-2: Corrective measures plan section 2- Detailed potential corrective measures (Guidance Document 2, EC, 2011b).

Name of Corrective Measure:

Measure A

No. of corrective measure

Comment: Please state the number of the corrective measure as found in the corrective measures overview table

No 1

Estimated timeframe needed for implementation

Comment: Please state how much time the full implementation of the measures is expected to take

Detailed description of measure

Comment: Please state on a detailed technical level, what the measure consists of: What is done where and when?

Rationale for the use of the measure

Comment: Please state why this measure is suited for the risk it is related to

Current status of the technique

Comment on the status of the technique or method, i.e. whether proven, commercial, under development, etc.