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MRCSP Phase I Geologic Characterization Report - Midwest ...

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44 CHARACTERIZATION OF GEOLOGIC SEQUESTRATION OPPORTUNITIES IN THE <strong>MRCSP</strong> REGION<br />

Table 19.—Potsdam Sandstone estimated effective<br />

CO 2-storage capacity by state (in gigatonnes)<br />

State Area (mi 2 ) Total<br />

Ohio 18 0.002<br />

Pennsylvania 9,280 1.704<br />

Total 9,298 1.706<br />

Table 21.—Rome trough sandstones estimated effective<br />

CO 2-storage capacity by state (in gigatonnes)<br />

State Area (mi 2 ) Total<br />

Eastern Kentucky 13,157 1.001<br />

Ohio 201 0.006<br />

West Virginia 5,094 0.221<br />

Total 18,452 1.228<br />

Table 20.—Unnamed Conasauga sandstones estimated effective<br />

CO 2-storage capacity by state (in gigatonnes)<br />

State Area (mi 2 ) Total<br />

Eastern Kentucky 25 0.001<br />

Michigan 409 0.164<br />

Ohio 21,185 3.469<br />

Pennsylvania 2,410 0.459<br />

West Virginia 943 0.0161<br />

Total 24,973 4.255<br />

Table 22.—Mt. Simon Formation estimated effective<br />

CO 2-storage capacity by state (in gigatonnes)<br />

State Area (mi 2 ) Total<br />

Eastern Kentucky 6,661 4.336<br />

Indiana 18,957 80.612<br />

Michigan 40,530 112.839<br />

Ohio 19,768 19.390<br />

Total 85,916 217.177<br />

by the St. Peter Sandstone and the “Clinton”/Medina/Tuscarora<br />

Sandstones. The deep saline formations with the smallest potential<br />

are the Potsdam Sandstone and basal sandstone in the Rome trough<br />

in eastern Kentucky. The low potentials stem from assigning these<br />

two aquifers very low porosities, since porosity generally decreases<br />

with depth, and both units are deeply buried. In addition, because<br />

of the lack of exploratory wells in many areas, such as in the deepest<br />

portion of the Appalachian basin in Pennsylvania, some areas<br />

contained no data and could not be mapped (see the structure and<br />

isopach maps of Appendix A). This also accounts for much of the<br />

small potential of the basal sandstones. The unnamed sandstones in<br />

the Conasuaga were also assigned a low porosity, since initial studies<br />

indicated the primary lithology of the Conasauga in eastern Ohio<br />

and western Pennsylvanian is a sandy or silty dolomite.<br />

It is perhaps useful to compare the estimated capacities in this<br />

study with some other assessments. An assessment of the Mt. Simon<br />

Sandstone (including areas outside <strong>MRCSP</strong>) by Gupta and others<br />

(2001) showed a capacity range of 160 to 800 gigatonnes based on<br />

a porosity range of 5 to 25 percent, net-to-gross-ratio of 50 to 95<br />

percent, and storage efficiency of 6 percent. In the same study, the<br />

capacity range for 8.5 percent porosity was 195 to 371 gigatonnes.<br />

This compares well with the estimated 10 percent capacity number<br />

of 217 gigatonnes for Mt. Simon in the <strong>MRCSP</strong> region in this<br />

study. Similarly, the Rose Run sandstone capacity range of 9 to 43<br />

gigatonnes of Gupta and others (2001) is comparable to the 49 gigatonnes<br />

estimated in the current study.<br />

Estimated CO 2 sequestration capacity in the Devonian Ohio<br />

Shale (Cleveland to Lower Huron Members) and equivalents in<br />

the Appalachian basin and the Antrim Shale in the Michigan basin<br />

ranges between 23.2 and 88.3 gigatonnes, varying between CO 2 adsorption<br />

rates of 22 and 84 standard cubic feet of gas per ton (U.S.)<br />

of shale. Capacity estimates for the black shales in eastern Kentucky<br />

represent only that part of the shale in the <strong>MRCSP</strong> region. The 90 th<br />

percentile figures calculated for Ohio, Pennsylvania, and West Virginia<br />

seems overly optimistic. The gray shales and intertonguing<br />

siltstones characteristic of the Devonian shale in these states may<br />

not have a sufficient organic matter content to adsorb such large volumes<br />

of CO 2. More realistically, the sequestration capacity is likely<br />

in the calculated range between the 10 th and 50 th percentiles. All of<br />

these estimates are, of course, contingent on the injectivity of CO 2<br />

into the shale, which is untested.<br />

For the oil-and-gas fields, the fields are separated into those that<br />

are less than 2,499 feet in depth and those that are greater than 2,500<br />

feet in depth (762 m). The 2500-foot depth cutoff roughly corresponds<br />

to the predicted transition from the gaseous phase to the super-critical<br />

phase of CO 2, which is approximately 260 times denser<br />

than the gaseous phase and, therefore, more desirable.<br />

Solubility Storage<br />

While solubility storage is described in this document, it is not applied<br />

in this study, since most of the initial sequestration will occur<br />

as volumetric storage. Instead, one representative calculation was<br />

conducted for the project. The solubility capacity was calculated for<br />

Mt. Simon Sandstone of Indiana, Michigan, and Ohio. The potential<br />

CO 2-storage capacity using the solubility calculation is in excess of<br />

83 gigatonnes, while the potential storage capacity using the volumetric<br />

calculations is over 217 gigatonnes, an increase by a factor<br />

of 2.6. However, an interesting phenomenon occurs in the solubility<br />

calculation. In the center of the Michigan basin, there is no solubility<br />

capacity. This is because the modeled salinity is too high to allow<br />

CO 2 to dissolve into the formation fluids. The high salinity, generally<br />

increasing salinities with depth, and the low solution rates indicate<br />

that solubility storage will not be a near-term factor in sequestering<br />

CO 2 in the <strong>MRCSP</strong> area. As a comparison, Dooley and others (2004)<br />

used the solubility approach to estimate that the total storage capacity<br />

in the Mt. Simon Sandstone, including all of the Illinois basin and<br />

the Appalachian basin is approximately 225 gigatonnes.

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