Testing subterranean water for a hazardous waste material repository
Techniques for determining the suitability of a subterranean formation as a hazardous waste repository include determining a neutron flux of a first isotope in a subterranean formation; calculating, based at least in part on the determined neutron flux of the first isotope, a predicted production rate of a second isotope in the subterranean formation; calculating a first ratio of the predicted production rate of the second isotope relative to a theoretical production rate of a stable form of the second isotope; measuring respective concentrations of the second isotope and the stable form of the second isotope in a subterranean water sample; calculating a second ratio of the measured concentration of the second isotope relative to the measured concentration of the stable form of the second isotope; and based on a comparison of the first and second ratios, determining that the subterranean formation is suitable as a hazardous waste repository.
1 . A method, comprising:
determining a first concentration of a particular radioisotope in a first water sample collected from a first rock layer at a first depth below a terranean surface from a first gamma ray log of the first rock layer, the particular radioisotope comprising at least one of naturally occurring I-129 or naturally occurring Cl-36 derived from one or more primordial radioisotopes present in the first rock layer and in a second rock layer at a second depth below the terranean surface that is deeper than the first depth;
determining a second concentration of the particular radioisotope in a second water sample collected from the second rock layer at the second depth below the terranean surface from a second gamma ray log of the second rock layer;
determining that the second concentration is greater than the first concentration by a specified percentage;
based on the determination that the second concentration is greater than the first concentration by the specified percentage, determining that the second rock layer is suitable as a human-unoccupiable hazardous waste storage repository; and
based on the determination that the second rock layer is suitable as the hazardous waste repository, forming an access drillhole of the hazardous waste repository from the terranean surface toward a depth in or under the second rock layer.
2 . The method of claim 1 , wherein the one or more primordial radioisotopes comprises at least one of U-238, U-235, Th-232, or K-40.
3 . The method of claim 2 , wherein the specified percentage is at least 50 percent.
4 . The method of claim 2 , wherein the one or more primordial radioisotopes comprises at least one of U-238, U-235, Th-232, or K-40.
5 . The method of claim 1 , wherein the specified percentage is at least 50 percent.
6 . The method of claim 1 , wherein the second rock layer comprises an impermeable layer.
7 . The method of claim 1 , wherein the second rock layer comprises a hydrocarbon-bearing formation.
8 . The method of claim 1 , further comprising initiating creation of the hazardous waste storage repository in or under the second rock layer.
9 . The method of claim 8 , wherein initiating creation of the hazardous waste storage repository in or under the second rock layer comprises forming a storage drillhole coupled to the access drillhole in or under the second rock layer, the storage drillhole comprising a hazardous waste storage area.
10 . The method of claim 9 , wherein the storage drillhole comprises at least one of a curved portion or a horizontal portion.
11 . The method of claim 9 , further comprising installing a casing in the access drillhole and the storage drillhole that extends from at or proximate the terranean surface, through the access drillhole and the storage drillhole, and into the hazardous waste material storage area of the storage drillhole.
12 . The method of claim 9 , further comprising storing hazardous waste material in the hazardous waste storage area.
13 . The method of claim 12 , wherein storing hazardous waste material in the hazardous waste storage area comprises:
moving a storage canister through an entry of the access drillhole that extends into the terranean surface, the entry at least proximate the terranean surface, the storage canister comprising an inner cavity sized to enclose the hazardous waste material;
moving the storage canister through the access drillhole and into the storage drillhole; and
moving the storage canister through the storage drillhole to the hazardous waste storage area.
14 . The method of claim 12 , wherein the hazardous waste material comprises spent nuclear fuel.
15 . The method of claim 12 , further comprising monitoring the hazardous waste material stored in the hazardous waste material storage area of the storage drillhole.
16 . The method of claim 15 , wherein monitoring the hazardous waste material stored in the hazardous waste material storage area of the storage drillhole comprises:
monitoring at least one variable associated with the storage canister from a sensor positioned proximate the hazardous waste material storage area; and
recording the monitored variable at the terranean surface.
17 . The method of claim 9 , further comprising forming a seal in at least one of the access drillhole or the storage drillhole that isolates the hazardous waste storage area from the entry of the access drillhole.
18 . The method of claim 1 , wherein the second rock layer comprises a thickness proximate the hazardous waste material storage area that inhibits diffusion of a hazardous waste material through the second rock layer for an amount of time that is based on a half-life of the hazardous waste material.
19 . The method of claim 1 , comprising collecting the first water sample from the first rock layer at the first depth below the terranean surface.
20 . The method of claim 19 , comprising collecting the second water sample from the second rock layer at the second depth below the terranean surface.