From Andy's presentation - Aims
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From Andy’s presentation • Aims – high-level techno-economic study – Framework for stakeholder engagement – Pre-feasibility study – May initiate licence applications for coal to liquids from brown coal
Project • 50 Mt per year • Anglo/Monash open cast coal with drying, gasification to make diesel with CO2 capture • Centralised capture/compression • Transport (40km onshore, 100km offshore) to Bass Strait offshore oil fields and deeper saline aquifers • Kingfish field: 15Mt per year for 40 years
Geology • Offshore Gippsland basin, Tertiary and Cretaceous with oil and gas fields • Kingfish Paleaocene and Eocene beach sand sediments with high permeabilities (up to 10D) and high productivities – 1 billion bbls • Reservoir quality is very good • Seal capacity – Supports 100m CO2 column heights – Intraformational seals 517m height – Top seals 360 column – Regional 395 m column height
Storage concept 1 • Migration will be west to east, updip • Seismically-mapped faults in intra units do not intersect migration pathway – 3 faults cut top seal – 7 intraformational faults – Most have medium to high reactivation potential – System is underpressured due to oil production • When CO2 reaches top (100-200yrs) of unconformity it will migrate east to west • CO2 moves under intraformational seals, leading to lots of residual gas trapping and solution trapping (25% after 200 yrs) • Some mineral trapping in immature reservoir underneath regional seal • Pressures always below initial reservoir (pre-production) pressures
Storage concept 2 • Hydrogeology – Onshore extraction – Offshore pressure sink due to depleted fields – This leads to strong hydrodynamic drive which balances east to west CO2 buoyancy-drive migration at top of Latrobe • Capacity, >600Mt so enough for storage plan • Injection will start at end of oil production but gas production will be ongoing at this stage
Modelling • 1Mt/yr per well, for 15 wells • Object modelling of shale interlayers within reservoir, small or large shales • Surfaces from 3D seismic • Permeabilities are averaged within formations • CO2 predicted to reach top seal after 200 years • Some potential for CO2 movement ot of field but remains trapped.
QRA for Kingfish • Outcome: total containment risks are below the proposed performance criteria • Discussion of terminology – Performance assessment or risk assessment – Consequences of impacts were not considered
Key lessons from techniques/frameworks used - Andy • RA aims – Transparent process – Interface with wider community – Allow assessment of safe, measurable, verifiable and economically sound • QRA using URS RISQUE method – Using expert panel, of 10 members, to identify risks events, likelihood and costs – Also includes cost-benefit analyses, impacts on communities • Fits with Aus/NZ risk standards • Qualitative descriptions of probability were transformed to mathematical probabilities • No performance indicators when started: – Therefore defined by CO2CRC – Containment: CO2 retention is 99% after 1000 years – Effectiveness: Any CO2 reduction to amount stored should
Latrobe Valley Evaluation of risk assessment
Strengths and weaknesses of datasets • Only publicly available data – 3D seismic coverage over field, larger coverage would have been useful – Cored wells within Kingfisher field – Lack of deep well control • Addressed through shale object modelling • High uncertainty, lack of pressure data – Lack of well density – Latest pressure information is unavailable, therefore relied on 15-year extrapolation • This increases uncertainty in containment and modelling but in terms of public concern this is unlikely to be important. • Access to commercially-sensitive information could be an issue in active oil/gas fields • Data that was missing – Poroperm data to constrain reservoir simulations – Need to drill deep wells to confirm stratigraphy and shale distribution – Stress tensors are not well constrained therefore less confidence from geomechanical modelling
Strengths and weaknesses of datasets • Lack of pressure profile – Could provide data on integrity of intraformational seals • Modelling highlighted lack of data on seal distribution and sensitivity to pathways • Well integrity – Currently only on classes of wells – Not evaluated individually – Some are open-hole, it is not known if these have self-sealed • Experts could be used to comment on data quality as well as identifying risk events • Have yet to consider timescales in terms of pressure evolution – Risk at highest during injection and have yet to identify pathways from wells during injection – Due to lack of detailed control of intraformational seal distribution and properties
Key lessons from techniques/frameworks used • Experts only from research organisation but should be extended to experts with extensive oil&gas experience • Could compare with additional expert panels • Plot containment against effectiveness risk indices for a number of storage sites, allows interpretation of confidence in risks as well as comparison against acceptable risk targets • Could perform sensitivity analyses to identify what drives confidence (e.g. expert opinion or parameter uncertainty…) • RA focussed on long-term issues – Containment but little work on near-surface leakage or impacts – Well treatments as classes (exploration, production, injection) – Development of stand-alone risk screening • Performance criteria is leakage from reservoir, this does not equate to marine or atmospheric flux
Key lessons from techniques/frameworks used • Should be clear that this was a research exercise not a RA for seeking a licence. • Not a formalised FEP approach – Due to lack of time and financial resources but might not have been done anyway – Use approach with which they were familiar – Allows rapid assessment, scenario definition and identification of principle risks • Performance Assessment (instead of RA) component completed by 1 person over 2 months and expert panel met twice for review – Provides regulators with digestible summary • If external stakeholders were involved than a more formal FEP audit may be required • May not identify all scenarios but key scenarios are probably included • Coupling between risk events not included • Wells were not evaluated individually • Lack of empirical data for leakage rates in faults and wells • Modelling has not been peer-reviewed
Inherent assumptions - general • Performance criteria (
Inherent assumptions - specific • Exploration wells, plugged and not re-entered or remediated – Assumed that they could leak, leakage rates are generic and are fixed – 200 t/yr/well for 14 wells over 500 years • Production & injection wells will be evaluated and remediated prior to abandonment therefore likelihood for leakage is lower, no opportunity for remediation after abandonment • No expected leakage through seal since a thick seal and retained oil for geological timescales • Overpressurisation will be avoided by monitoring and could get some fluid migration into field due to depletion • Seismic activity has been reviewed – Assume self-sealing of any reactivated fault with some short-term leakage • Identification of seismically resolvable faults does not indicate potential migration to surface
Confidence in results • Publicly available data constrains confidence in some results – No access to wells, production data or pressure data etc – No operator participation • Internal panel experts did not necessarily have wide oil&gas expertise – estimates of confidence may be different from other experts • Could repeat expert panel process with different experts • Based on confidence in data, is it right to make assertions to non-experts about Gippsland containment? – A priori – an oilfield – It is recognised that well integrity remains the key issue. • The impacts of faster vertical migration could be investigated • Uncertainty ranges indicated from this approach for other sites possibly too narrow.
Confidence Building • Explicit statements of known parameters, processes and their uncertainty, weaknesses • This leads to a definition of how to address these weaknesses – Monitoring programmes could be developed to address weaknesses identified. • The RA was made publicly available with strong community engagement – Broad support – Some issues from agricultural communities regarding water supply (storage was good, reducing groundwater drawdown) – Potential for onshore leakage was raised and then adequately addressed
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