Patent Number: 
Section: claims

1. A method for disposing nuclear waste using a deep geological repository, comprising the following steps:drilling a well down to a granite stratum;forming a fracture in the granite stratum by injecting liquid for forming fracture into the underground granite stratum;injecting a sand-carrying feed liquid containing powder nuclear waste or liquid nuclear waste to the fracture in the underground granite stratum by a high-pressure injection pump, so that the sand-carrying feed liquid stays in the fracture of the granite stratum for coagulating, and after disposal a wellhead is sealed by wellhead cementing concrete, thereby permanently storing the nuclear waste in the fracture of the underground granite stratum, and achieving the purpose of effective disposal to the nuclear waste; andadding an active agent into the liquid for forming fracture, wherein the active agent is composed of a surfactant and oxalic acid in a ratio of 4.5 to 5:1, in which the surfactant is linear alkylbenzene sulfonates, tetrapropylene benzene sulfonate, dioctyl sulfosuccinate, sodium dodecyl benzene sulfonate or sodium stearyl sulfate, and the active agent is added in an amount equal to 2 to 3.5% of water in the liquid. 2. The method for disposing nuclear waste using a deep geological repository of claim 1, further comprising the following steps:sampling the granite stratum; andforming the fracture in the granite stratum, wherein the pressure is set according to the density of the granite stratum, and the pressure is set at 40 to 140 MPa/cm2. 3. A method for disposing nuclear waste using a deep geological repository, comprising the following steps:drilling a well down to a granite stratum;forming a fracture in the granite stratum by injecting liquid for forming fracture into the underground granite stratum; andinjecting a sand-carrying feed liquid containing powder nuclear waste or liquid nuclear waste to the fracture in the underground granite stratum by a high-pressure injection pump, so that the sand-carrying feed liquid stays in the fracture of the granite stratum for coagulating, and after disposal a wellhead is sealed by wellhead cementing concrete, thereby permanently storing the nuclear waste in the fracture of the underground granite stratum, and achieving the purpose of effective disposal to the nuclear waste; andweighing and mixing the following substances to form the sand-carrying feed liquid: 2 to 4 parts of polyacrylamide, 45 to 55 parts of cementing cement, 1.5 to 2.5 parts of a profile control agent, 2 to 8 parts of quartz sand, 0.5 to 1.5 parts of a high-temperature resistant reagent, 20 to 30 parts of a nuclear waste, 0.5 to 5 parts of a cement retardant for prolonging the coagulating time or 2 to 5 parts of a coagulant for shortening the coagulating time, and 30 to 60 parts of water. 4. The method for disposing nuclear waste using a deep geological repository of claim 1, wherein the method requires a remote computer-assisted automated control and a robotic operation. 5. The method for disposing nuclear waste using a deep geological repository of claim 3, further comprising the following step:adding an active agent into the liquid for forming fracture, wherein the active agent is composed of a surfactant and oxalic acid in a ratio of 4.5 to 5:1, in which the surfactant is linear alkylbenzene sulfonates, tetrapropylene benzene sulfonate, dioctyl sulfosuccinate, sodium dodecyl benzene sulfonate or sodium stearyl sulfate, and the active agent is added in an amount equal to 2 to 3.5% of water in the liquid. 6. The method for disposing nuclear waste using a deep geological repository of claim 5, further comprising the following step:injecting the sand-carrying feed liquid to the fracture in the underground granite stratum by the high-pressure injection pump through a high-pressure pipeline and a conveying pipeline in the well, wherein the injection pressure of the high-pressure injection pump is set at 30 to 70 MPa, so that water in the fracture of the granite stratum expands in a horizontal direction of the stratum under the effect of the pressure of the sand-carrying feed liquid. 7. A method for disposing nuclear waste using a deep geological repository, comprising the following steps:Step I. drilling a well down to a granite stratum;Step II. forming a fracture in the granite stratum using a device by injecting liquid into the underground granite stratum through a liquid supply manifold of a disposal device, a liquid supply pump, a supply-discharge pump connecting pipe, a output pump, a output manifold, a mixed liquid material conveying pipeline, a high-pressure injection pump, a high-pressure pipeline and a conveying pipeline in the well, with the high-pressure injection pump set at 40 to 140 MPa/cm2, so as to form the fracture in the granite stratum, wherein during this step a first valve is closed and a second valve on the supply-discharge pump connecting pipe is opened;Step III. weighing 2 to 4 parts of polyacrylamide, 45 to 55 parts of cementing cement, 1.5 to 2.5 parts of a profile control agent, 2 to 8 parts of quartz sand, 0.5 to 1.5 parts of a high-temperature resistant reagent, 20 to 30 parts of a radioactive substance, 0.5 to 5 parts of a cement retardant or 2 to 5 parts of a coagulant, and 30 to 60 parts of water;Step IV. using the device, sending the quartz sand and the cementing cement of Step III through a raw material conveyor of the device to a raw material mixer of the device, sending the radioactive substance through a powder waste conveyor or the liquid waste conveying pipeline to the raw material mixer of the device, sending the profile control agent, the high-temperature resistant reagent, the cement retardant, and the coagulant through the additive tank of the device to the raw material mixer, sending the water through the liquid supply manifold by the liquid supply pump to the raw material mixer, and mixing uniformly, wherein during this step, the first valve is opened, and the second valve on the supply-discharge pump connecting pipe is closed;Step V. sending the sand-carrying feed liquid mixed in Step IV by the output pump of the device to the output manifold and then to the mixed liquid material conveying pipeline through the output manifold; andStep VI. injecting the sand-carrying feed liquid in the mixed liquid material conveying pipeline in Step V to the fracture in the underground granite stratum by the high-pressure injection pump through the high-pressure pipeline and the conveying pipeline in the well, with the injection pressure of the high-pressure injection pump set at 30 to 70 MPa, so that water in the fracture of the granite stratum expands in a horizontal direction of the stratum under the effect of the pressure of the sand-carrying feed liquid, and the sand-carrying feed liquid stays in the fracture of the granite stratum for coagulating, and after disposal the wellhead is sealed by wellhead cementing concrete, thereby permanently storing the nuclear waste in the fracture of the underground granite stratum, and achieving the purpose of effective disposal to the nuclear waste. 8. The method for disposing nuclear waste using a deep geological repository of claim 7, further comprising adding an active agent into the fracture-forming liquid of Step II, wherein the active agent is composed of a surfactant and oxalic acid in a ratio of 4.5 to 5:1, in which the surfactant is linear alkylbenzene sulfonates, tetrapropylene benzene sulfonate, dioctyl sulfosuccinate, sodium dodecyl benzene sulfonate or sodium stearyl sulfate, and the active agent is added in an amount equal to 2 to 3.5% of the water. 9. The method for disposing nuclear waste using a deep geological repository of claim 7, wherein, in Step III, when the nuclear waste is powder waste, the liquid waste conveying pipeline of the device is closed, and when the nuclear waste is liquid waste, the powder waste conveyor of the device is closed. 10. The method for disposing nuclear waste using a deep geological repository of claim 7, wherein, in Step III, the weighing includes weighing 3 parts of polyacrylamide, 50 parts of the cementing cement, 2 parts of the profile control agent, 5 parts of the quartz sand, 1 part of the high-temperature resistant reagent, 25 parts of the radioactive substance, 3 parts of the cement retardant or 3.5 parts of the coagulant, and 45 parts of the water; and in Step VI, the injection pressure of the high-pressure injection pump is 50 MPa. 11. The method for disposing nuclear waste using a deep geological repository of claim 7, wherein the profile control agent, the high-temperature resistant reagent, the cement retardant and the coagulant are all preparations usually used in cement applications. 12. The method for disposing nuclear waste using a deep geological repository of claim 7, further comprising the steps:sampling the granite stratum; andforming the fracture in the granite stratum, wherein the pressure is set according to the density of the granite stratum. 13. The method for disposing nuclear waste using a deep geological repository of claim 7, wherein the method requires a remote computer-assisted automated control and a robotic operation.