Patent Number: 
Section: claims

1. A nuclear waste hazardous material storage bank, comprising:a wellbore extending into the Earth and comprising an entry at least proximate a terranean surface, the wellbore comprising a substantially vertical portion, a transition portion, and a substantially horizontal portion;a storage area coupled to the substantially horizontal portion of the well bore, the storage area within or below an impermeable, hydrocarbon bearing shale formation, the storage area vertically isolated, by the hydrocarbon bearing shale formation, from a subterranean zone that comprises mobile water, the shale formation comprising a diffusion barrier to a radioactive gas isotope of the nuclear waste hazardous material;a storage container positioned in the storage area, the storage container sized to fit from the wellbore entry through the substantially vertical, the transition, and the substantially horizontal portions of the wellbore, and into the storage area, the storage container comprising an inner cavity that encloses a nuclear waste hazardous material; anda seal positioned in the wellbore, the seal isolating the storage area of the wellbore from the entry of the wellbore. 2. The nuclear waste hazardous material storage bank of claim 1, wherein the storage area is formed below the hydrocarbon bearing shale formation and is vertically isolated from the subterranean zone that comprises mobile water by the hydrocarbon bearing shale formation. 3. The nuclear waste hazardous material storage bank of claim 1, wherein the storage area is formed within the hydrocarbon bearing shale formation, and is vertically isolated from the subterranean zone that comprises mobile water by at least a portion of the hydrocarbon bearing shale formation. 4. The nuclear waste hazardous material storage bank of claim 1, wherein the hydrocarbon bearing shale formation comprises a permeability of less than about 0.001 millidarcys. 5. The nuclear waste hazardous material storage bank of claim 1, wherein the hydrocarbon bearing shale formation comprises a brittleness of less than about 10, where brittleness comprises a ratio of compressive stress of the hydrocarbon bearing shale formation to tensile strength of the shale formation. 6. The nuclear waste hazardous material storage bank of claim 1, wherein the hydrocarbon bearing shale formation comprises a thickness proximate the storage area of at least about 100 feet. 7. The nuclear waste hazardous material storage bank of claim 1, wherein the hydrocarbon bearing shale formation comprises a thickness proximate the storage area that inhibits diffusion of the nuclear waste hazardous material that escapes the storage container through the hydrocarbon bearing shale formation for an amount of time that is a multiple of a half-life of a radioactive component of the nuclear waste hazardous material. 8. The nuclear waste hazardous material storage bank of claim 1, wherein the hydrocarbon bearing shale formation comprises about 20 to 30% weight of clay or about 20 to 30% weight of organic matter. 9. The nuclear waste hazardous material storage bank of claim 1, wherein the nuclear waste hazardous material comprises spent nuclear fuel. 10. The nuclear waste hazardous material storage bank of claim 1, further comprising at least one casing assembly that extends from at or proximate the terranean surface, through the wellbore, and into the storage area. 11. The nuclear waste hazardous material storage bank of claim 1, wherein the storage container comprises a connecting portion configured to couple to at least one of a downhole tool string or another storage container. 12. A method for storing nuclear waste hazardous material, comprising:moving a storage container through an entry of a wellbore that extends into a terranean surface, the entry at least proximate the terranean surface, the storage container comprising an inner cavity that encloses nuclear waste hazardous material;moving the storage container through the wellbore that comprises a substantially vertical portion, a transition portion, and a substantially horizontal portion, the storage container sized to fit from the wellbore entry through the substantially vertical, the transition, and the substantially horizontal portions of the wellbore;moving the storage container into a storage area that is coupled to the substantially horizontal portion of the well bore, the storage area located within or below an impermeable, hydrocarbon-bearing shale formation and vertically isolated, by the hydrocarbon-bearing shale formation, from a subterranean zone that comprises mobile water, the shale formation comprising a diffusion barrier to a radioactive gas isotope of the nuclear waste hazardous material; andforming a seal in the wellbore that isolates the storage portion of the wellbore from the entry of the wellbore. 13. The method of claim 12, wherein the storage area is formed below the hydrocarbon-bearing shale formation and is vertically isolated from the subterranean zone that comprises mobile water by the hydrocarbon-bearing shale formation. 14. The method of claim 12, wherein the storage area is formed within the hydrocarbon-bearing shale formation, and is vertically isolated from the subterranean zone that comprises mobile water by at least a portion of the hydrocarbon-bearing shale formation. 15. The method of claim 12, wherein hydrocarbon-bearing the shale formation comprises geological properties comprising two or more of:a permeability of less than about 0.001 millidarcys;a brittleness of less than about 10, where brittleness comprises a ratio of compressive stress of the hydrocarbon-bearing shale formation to tensile strength of the hydrocarbon-bearing shale formation;a thickness proximate the storage area of at least about 100 feet; orabout 20 to 30% weight of organic material or about 20 to 30% weight of clay. 16. The method of claim 12, wherein the nuclear waste hazardous material comprises spent nuclear fuel. 17. The method of claim 12, wherein the wellbore further comprises at least one casing that extends from at or proximate the terranean surface, through the wellbore, and into the storage area. 18. The method of claim 12, further comprising:prior to moving the storage container through the entry of the wellbore that extends into the terranean surface, forming the wellbore from the terranean surface to the hydrocarbon-bearing shale formation. 19. The method of claim 18, further comprising installing a casing in the wellbore that extends from at or proximate the terranean surface, through the wellbore, and into the storage area. 20. The method of claim 19, further comprising cementing the casing to the wellbore. 21. The method of claim 18, further comprising, subsequent to forming the wellbore, producing hydrocarbon fluid from the hydrocarbon-bearing shale formation, through the wellbore, and to the terranean surface. 22. The method of claim 12, further comprising:removing the seal from the wellbore; andretrieving the storage container from the storage area to the terranean surface. 23. The method of claim 12, further comprising:monitoring at least one variable associated with the storage container from a sensor positioned proximate the storage area; andrecording the monitored variable at the terranean surface. 24. The method of claim 23, wherein the monitored variable comprises at least one of radiation level, temperature, pressure, presence of oxygen, presence of water vapor, presence of liquid water, acidity, or seismic activity. 25. The method of claim 23, further comprising, based on the monitored variable exceeding a threshold value:removing the seal from the wellbore; andretrieving the storage container from the storage area to the terranean surface. 26. A spent nuclear fuel storage system, comprising:a directional wellbore formed from a terranean surface, through a first subterranean layer, and into a second subterranean layer deeper than the first subterranean layer, the first subterranean layer comprising a rock formation that includes a source of mobile water, the second subterranean layer comprising an impervious, hydrocarbon bearing shale formation, the shale formation fluidly isolating a portion of the directional wellbore formed within the shale formation from the first subterranean layer, the shale formation comprising a diffusion barrier to a radioactive gas isotope of the nuclear waste hazardous material;a container configured to be moved through the directional wellbore into the portion of the directional wellbore formed within the shale formation, the container comprising a volume enclosed by a housing configured to store a plurality of spent nuclear fuel pellets; anda plug set in the directional wellbore between the portion of the directional wellbore formed within the shale formation and the terranean surface. 27. The spent nuclear fuel storage system of claim 26, further comprising a monitoring system, comprising a monitoring control system communicably coupled to one or more systems positioned proximate the container. 28. The spent nuclear fuel storage system of claim 26, further comprising a tubular liner constructed in the directional wellbore and sealed against a wall of the directional wellbore. 29. The nuclear waste hazardous material storage bank of claim 1, wherein at least a part of the substantially horizontal portion of the wellbore defines a volume that comprises the storage area, and the part of the substantially horizontal portion of the wellbore is formed within the hydrocarbon-bearing shale formation. 30. The method of claim 12, further comprising repairing perforations in a production casing in the wellbore prior to moving the storage container into the storage area. 31. The nuclear waste hazardous material storage bank of claim 1, wherein the hydrocarbon-bearing shale formation is at a true vertical depth of between 3000 and 12,000 feet. 32. The nuclear waste hazardous material storage bank of claim 1, wherein the radioactive gas isotope comprises tritium. 33. The nuclear waste hazardous material storage bank of claim 1, wherein the diffusion barrier comprises a diffusion time of the radioactive gas isotope of the nuclear waste hazardous material of a multiple of a half-life of the radioactive gas. 34. The nuclear waste hazardous material storage bank of claim 33, wherein the multiple is between thirty and fifty times the half-life of the radioactive gas isotope.