A number of variables determine whether a tool is effective. In this study, we focus on those variables that are site specific. However, to make a clear evaluation, we have prepared a list of factors that influence whether a tool is effective, so that those that are not site specific can be dealt with via specifying best available technologies.
Many variables interact to determine whether a tool is effective, adding complexity to our assessment. In this study we force a rather artificial single-variable approach on the assessment. In addition, we have initially selected sets of variables that we think will have a strong effect on tool sensitivity, which is subject to revision as the assessment matures.
One major difficulty in determining the appropriateness of tools is determining the appropriate signal threshold that it is desirable to detect. EPA rules provide no threshold below which a leakage or mismatch with model results are considered negligible.
The table below provides, for each tool type, a preliminary list of site-specific and non-site-specific variables that impact tool sensitivity. In the next year this matrix will be assessed more deeply via literature review, expert panel review, and where needed in a numerical modeling of tool sensitivity. This version of the table is assembled for the purpose of discussion.
Preliminary inventory of site-specific factors that influence tool sensitivity compared with general factors that are the same at all sites.
Compartment tested |
Non-site-specific factors that influence tool sensitivity* |
Site-specific factors that influence tool sensitivity* |
Notes |
CO2 concentration of air |
Analytical detection limits
Sample height
Location of sample point with respect to leakage path |
Ambient daily and seasonal variation
Across-site variation in ambient CO2 emissions
Dilution between emission point and sample point |
|
Natural or introduced CO2 tracers sampled in air |
Analytical detection limits
Lab/sampler contamination
Location of sample point with respect to leakage path |
Difference between ambient composition and injectate composition
Stability of tracer during leakage process, dissolution, sorption processes |
Even introduced tracers have some background in environment |
Percent CO2 in soil gas (relative to O2 and N2) |
Analytical detection limits
Well construction—atmospheric contamination |
Ratio of leakage rate to natural cycling processes
In situ CO2 production, release, dissolution, sorption processes |
Collecting O2 and N2 provides process information |
Natural CO2 tracers (δC13, noble gasses) sampled in soil gas |
Analytical detection limits
Lab/sampler contamination
Location of sample point with respect to leakage path |
Difference between ambient composition and injectate composition
Stability of tracer during leakage process |
These tracers may be more conservative and therefore more sensitive than CO2 itself. |
Introduced CO2 tracers (PFT) sampled in soil gas |
Analytical detection limits
Lab/sampler contamination
Location of sample point with respect to leakage path |
Stability of tracer during leakage process, e.g., dissolution, sorption during transport |
Even introduced tracers have some background in environment |
Groundwater salinity |
Well-completion issues, perforated interval, mixing along sand pack,
Analytical detection limits
Location of well sample point with respect to leakage path, considering density, mixing |
Ambient variably in salinity
Aquifer flow rate and process, mixing |
Might use near-surface conductivity to sample a larger area |
Groundwater/above-zone monitoring interval (AZMI) pH |
Analytical detection limits
Sampling process, outgassing
Location of well sample point with respect to leakage path, considering density, mixing |
pH change with respect to introduced CO2, buffering
Ambient variably in pH
Aquifer flow rate and process, mixing |
pH is sensitive to sampling procedure, especially temperature, pressure, and outgassing |
Groundwater/AZMI DOC/DIC |
Analytical detection limits
Location of well sample point with respect to leakage path, considering density, mixing |
Ambient variably in DOC/DIC
Aquifer flow rate and process, mixing
Sorption and mineral reaction |
Best used in combination with other measurements |
Groundwater/AZMI Head-space gas |
Analytical detection limits
Location of well sample point with respect to leakage path, considering density, mixing |
Ambient variably in free/dissolved CO2
Aquifer flow rate and process, mixing
Sorption and mineral reaction |
Head gas is sensitive to temperature, outgassing, sampling procedure
Best used in combination with other measurements |
Groundwater/AZMI major and minor elements |
Analytical detection limits
Location of well sample point with respect to leakage path, considering density, mixing |
Ambient variably in major and minor elements
Aquifer flow rate and process, mixing
Sorption and mineral reaction |
Sensitive to lab detection limits, proper sampling, stabilization and curation for various elements and compounds; best used in combination with other measurements constituents |
Confined aquifer/ AZMI pressure |
Gage sensitivity, depth error in positioning gage, land surface elevation error.
Well completion, perforations, well fluids
Location of well measurement point with respect to leakage path |
Aquifer ambient variability to recharge, barometric pressure, tides, etc., fluid density; monitored zone thickness, transmissivity, storativity |
|
Pressure in injection zone |
Gage sensitivity, depth error in positioning gage
Well completion, perforations, well fluids |
Ambient variability to recharge, barometric pressure, tides, etc., fluid density; zone thickness, transitivity, storativity |
|
Tubing pressure at wellhead |
Noise from daily thermal variations
Well completion, perforations, well fluids |
Rate of breakthrough.
Dissolved CO2 may complicate response
Non-CO2 fluid changes will complicate response |
|
Pulsed neutron logging to detect CO2 saturation in injection zone or in AZMI |
Well completion, perforations, well fluids
Tool construction and deployment
Processing of sigma
Near-well-bore perturbations |
Salinity of ambient fluids
Saturation of CO2
Noise
Stratigraphic complexity, bed thickness |
Complex processing is possible |
Resistivity logging to detect CO2 saturation in injection zone or in AZMI |
Well completion, perforations, well fluids
Tool construction and deployment
Processing
Near-well-bore perturbations |
Salinity of ambient fluids.
Saturation of CO2
Noise
Stratigraphic complexity, bed thickness |
Not used in steel wells |
Sonic logging to detect CO2 saturation in injection zone or AZMI |
Well completion, perforations, well fluids
Tool construction and deployment
Processing of signal
Near-well-bore perturbations |
Change in impedance and velocity with change in CO2 saturation
Stratigraphic complexity, bed thickness
Saturation of CO2
Noise |
Tool size can limit deployment |
2-D seismic profiling to locate plume edge |
Source selection, receiver deployment, many variations in set-up
Processing |
Static error
Signal:noise ratio
Change in impedance and velocity with change in CO2 saturation
Stratigraphic complexity, bed thickness, depth
Saturation of CO2 |
Multiple variables intersect complexly
Focus area for CCP study |
Walk-away VSP to locate plume edge |
Source selection, receiver deployment, many variations in set-up
Processing |
Static error
Signal: noise ratio
Change in impedance and velocity with change in CO2 saturation
Stratigraphic complexity, bed thickness
Saturation of CO2 |
Multiple variables intersect complexly
Higher vertical resolution; limited horizontal coverage
Focus area for CCP study |
3-D seismic survey for locate plume edge |
Source selection, receiver deployment, many variations in set-up
Processing |
Static error
Signal: noise ratio
Change in impedance and velocity with change in CO2 saturation.
Stratigraphic complexity, bed thickness, depth
Saturation of CO2 |
Multiple variables intersect complexly
Focus area for CCP study |
Surface gravity |
Consideration deferred |
|
Focus area for CCP study |
Surface electrical and magnetic techniques |
Consideration deferred |
|
Focus area for CCP study |