cy assumes that compliance can be determined based upon "best estimate" predictions (e.g., the mean or the median of the appropriate distribution, whichever is higher). Institutional Controls. To comply with §191.14(a), the implementing agency will assume that none of the active institutional controls prevent or reduce radionuclide releases for more than 100 years after disposal. However, the Federal Government is committed to retaining ownership of all disposal sites for spent nuclear fuel and high-level and transuranic radioactive wastes and will establish appropriate markers and records, consistent with $191.14(c). The Agency assumes that, as long as such passive institutional controls endure and are understood, they: (1) Can be effective in deterring systematic or persistent exploitation of these disposal sites; and (2) can reduce the likelihood of inadvertent, intermittent human intrusion to a degree to be determined by the implementing agency. However, the Agency believes that passive institutional controls can never be assumed to eliminate the chance of inadvertent and intermittent human intrusion into these disposal sites. Consideration of Inadvertent Human Intrusion into Geologic Repositories. The most speculative potential disruptions of a mined geologic repository are those associated with inadvertent human intrusion. Some types of intrusion would have virtually no effect on a repository's containment of waste. On the other hand, it is possible to conceive of intrusions (involving widespread societal loss of knowledge regarding radioactive wastes) that could result in major disruptions that no reasonable repository selection or design precautions could alleviate. The Agency believes that the most productive consideration of inadvertent intrusion concerns those realistic possibilities that may be usefully mitigated by repository design, site selection, or use of passive controls (although passive institutional controls should not be assumed to completely rule out the possibility of intrusion). Therefore, inadvertent and intermittent intrusion by exploratory drilling for resources (other than any provided by the disposal system itself) can be the most severe intrusion scenario assumed by the implementing agencies. Furthermore, the implementing agencies can assume that passive institutional controls or the intruders' own exploratory procedures are adequate for the intruders to soon detect, or be warned of, the incompatibility of the area with their activi drilling. However, the Agency assumes that the likelihood of such inadvertent and intermittent drilling need not be taken to be greater than 30 boreholes per square kilometer of repository area per 10,000 years for geologic repositories in proximity to sedimentary rock formations, or more than 3 boreholes per square kilometer per 10,000 years for repositories in other geologic formations. Furthermore, the Agency assumes that the consequences of such inadvertent drilling need not be assumed to be more severe than: (1) Direct release to the land surface of all the ground water in the repository horizon that would promptly flow through the newly created borehole to the surface due to natural lithostatic pressure-or (if pumping would be required to raise water to the surface) release of 200 cubic meters of ground water pumped to the surface if that much water is readily available to be pumped; and (2) creation of a ground water flow path with a permeability typical of a borehole filled by the soil or gravel that would normally settle into an open hole over time-not the permeability of a carefully sealed borehole. [50 FR 38084, Sept. 19, 1985. Redesignated and amended at 58 FR 66415, Dec. 20, 1993] Subpart D-Standards for Management of Uranium Byproduct Materials Pursuant 192.30 Applicability. 192.31 Definitions and cross-references. 192.33 Corrective action programs. TABLE A TO SUBPART D Subpart E-Standards for Management of 192.40 Applicability. 192.41 Provisions. 192.42 Substitute provisions. APPENDIX I TO PART 192-LISTED CONSTITU- AUTHORITY: Sec. 275 of the Atomic Energy SOURCE: 48 FR 602, Jan. 5, 1983, unless oth- Subpart A-Standards for the active Materials from Inactive $192.00 Applicability. This subpart applies to the control of residual radioactive material at designated processing or depository sites under section 108 of the Uranium Mill Tailings Radiation Control Act of 1978 (henceforth designated "the Act"), and to restoration of such sites following any use of subsurface minerals under section 104(h) of the Act. § 192.01 unprocessed ores or low-grade materials. (b) Remedial action means any action performed under section 108 of the Act. (c) Control means any remedial action intended to stabilize, inhibit future misuse of, or reduce emissions or effluents from residual radioactive materials. (d) Disposal site means the region within the smallest perimeter of residual radioactive material (excluding cover materials) following completion of control activities. (e) Depository site means a site (other than a processing site) selected under Section 104(b) or 105(b) of the Act. (f) Curie (Ci) means the amount of radioactive material that produces 37 billion nuclear transformation per second. One picocurie (pCi) = 10 −12Ci. (g) Act means the Uranium Mill Tailings Radiation Control Act of 1978, as amended. (h) Administrator means the Administrator of the Environmental Protection Agency. (i) Secretary means the Secretary of Energy. (j) Commission means the Nuclear Regulatory Commission. (k) Indian tribe means any tribe, band, clan, group, pueblo, or community of Indians recognized as eligible for services provided by the Secretary of the Interior to Indians. (1) Processing site means: (1) Any site, including the mill, designated by the Secretary under Section 102(a)(1) of the Act; and (2) Any other real property or improvement thereon which is in the vicinity of such site, and is determined by the Secretary, in consultation with the Commission, to be contaminated with residual radioactive materials derived from such site. (m) Tailings means the remaining portion of a metal-bearing ore after some or all of such metal, such as uranium, has been extracted. (n) Disposal period means the period of time beginning March 7, 1983 and ending with the completion of all subpart A requirements specified under a plan for remedial action except those specified in § 192.03 and § 192.04. (0) Plan for remedial action means a written plan (or plans) for disposal and cleanup of residual radioactive materials associated with a processing site that incorporates the results of site characterization studies, environmental assessments or impact statements, and engineering assessments so as to satisfy the requirements of subparts A and B of this part. The plan(s) shall be developed in accordance with the provisions of Section 108(a) of the Act with the concurrence of the Commission and in consultation, as appropriate, with the Indian Tribe and the Secretary of Interior. (p) Post-disposal period means the period of time beginning immediately after the disposal period and ending at termination of the monitoring period established under §192.03. (q) Groundwater means water below the ground surface in a zone of saturation. (r) Underground source of drinking water means an aquifer or its portion: (1)(1) Which supplies any public water system as defined in § 141.2 of this chapter; or (ii) Which contains a sufficient quantity of groundwater to supply a public water system; and (A) Currently supplies drinking water for human consumption; or (B) Contains fewer than 10,000 mg/l total dissolved solids; and (2) Which is not an exempted aquifer as defined in § 144.7 of this chapter. [48 FR 602, Jan. 5, 1983, as amended at 60 FR 2865, Jan. 11, 1995] § 192.02 Standards. Control of residual radioactive materials and their listed constituents shall be designed1 to: (a) Be effective for up to one thousand years, to the extent reasonably achievable, and, in any case, for at least 200 years, and, (b) Provide reasonable assurance that releases of radon-222 from residual radioactive material to the atmosphere will not: 1 Because the standard applies to design, monitoring after disposal is not required to demonstrate compliance with respect to §192.02(a) and (b). (1) Exceed an average2 release rate of 20 picocuries per square meter per second, or (2) Increase the annual average concentration of radon-222 in air at or above any location outside the disposal site by more than one-half picocurie per liter. (c) Provide reasonable assurance of conformance with the following groundwater protection provisions: (1) The Secretary shall, on a site-specific basis, determine which of the constituents listed in Appendix I to Part 192 are present in or reasonably derived from residual radioactive materials and shall establish a monitoring program adequate to determine background levels of each such constituent in groundwater at each disposal site. (2) The Secretary shall comply with conditions specified in a plan for remedial action which includes engineering specifications for a system of disposal designed to ensure that constituents identified under paragraph (c)(1) of this section entering the groundwater from a depository site (or a processing site, if residual radioactive materials are retained on the site) will not exceed the concentration limits established under paragraph (c)(3) of this section (or the supplemental standards established under §192.22) in the uppermost aquifer underlying the site beyond the point of compliance established under paragraph (c)(4) of this section. (3) Concentration limits: (i) Concentration limits shall be determined in the groundwater for listed constituents identified under paragraph (c)(1) of this section. The concentration of a listed constituent in groundwater must not exceed: (A) The background level of that constituent in the groundwater; or (B) For any of the constituents listed in Table 1 to subpart A, the respective value given in that Table if the back 2This average shall apply over the entire surface of the disposal site and over at least a one-year period. Radon will come from both residual radioactive materials and from materials covering them. Radon emissions from the covering materials should be estimated as part of developing a remedial action plan for each site. The standard, however, applies only to emissions from residual radioactive materials to the atmosphere. lease rated ter per se verage co air at he dispos picocuri Surance followin sions: a site-spe f the cor I to Par y deriv material ring e bact stitue site. ply wit or reme neering dispos ituent of the er fr g st are ed th under or the ished uifer ut of ground level of the constituent is below (C) An alternate concentration limit (ii)(A) The Secretary may apply an alternate concentration limit if, after considering remedial or corrective actions to achieve the levels specified in paragraphs (c)(3)(i)(A) and (B) of this section, he has determined that the constituent will not pose a substantial present or potential hazard to human health and the environment as long as the alternate concentration limit is not exceeded, and the Commission has concurred. (B) In considering the present or potential hazard to human health and the environment of alternate concentration limits, the following factors shall be considered: (1) Potential adverse effects on groundwater quality, considering: (i) The physical and chemical characteristics of constituents in the residual radioactive material at the site, including their potential for migration; (ii) The hydrogeological characteristics of the site and surrounding land; (iii) The quantity of groundwater and the direction of groundwater flow; (iv) The proximity and withdrawal rates of groundwater users; (v) The current and future uses of groundwater in the region surrounding the site; (vi) The existing quality of groundwater, including other sources of contamination and their cumulative impact on the groundwater quality; (vii) The potential for health risks caused by human exposure to constituents; (viii) The potential damage to wildlife, crops, vegetation, and physical structures caused by exposure to constituents; (ix) The persistence and permanence of the potential adverse effects; (x) The presence of underground sources of drinking water and exempted aquifers identified under $144.7 of this chapter; and (2) Potential adverse effects on hydraulically-connected surface-water quality, considering: (i) The volume and physical and chemical characteristics of the residual radioactive material at the site; (ii) The hydrogeological characteristics of the site and surrounding land; (iii) The quantity and quality of groundwater, and the direction of groundwater flow; (iv) The patterns of rainfall in the region; (v) The proximity of the site to surface waters; (vi) The current and future uses of surface waters in the region surrounding the site and any water quality standards established for those surface waters; (vii) The existing quality of surface water, including other sources of contamination and their cumulative impact on surface water quality; (viii) The potential for health risks caused by human exposure to constituents; (ix) The potential damage to wildlife, crops, vegetation, and physical structures caused by exposure to constituents; and (x) The persistence and permanence of the potential adverse effects. (4) Point of compliance: The point of compliance is the location at which the groundwater concentration limits of paragraph (c)(3) of this section apply. The point of compliance is the intersection of a vertical plane with the uppermost aquifer underlying the site, located at the hydraulically downgradient limit of the disposal area plus the area taken up by any liner, dike, or other barrier designed to contain the residual radioactive material. (d) Each site on which disposal occurs shall be designed and stabilized in a manner that minimizes the need for future maintenance. [60 FR 2865, Jan. 11, 1995] § 192.03 Monitoring. A groundwater monitoring plan shall be implemented, to be carried out over a period of time commencing upon completion of remedial actions taken to comply with the standards in §192.02, and of a duration which is adequate to demonstrate that future performance of the system of disposal can reasonably be expected to be in accordance with the design requirements of §192.02(c). This plan and the length of the monitoring period shall be modified to incorporate any corrective actions required under §192.04 or §192.12(c). [60 FR 2866, Jan. 11, 1995] §192.04 Corrective Action. If the groundwater concentration limits established for disposal sites under provisions of §192.02(c) are found or projected to be exceeded, a corrective action program shall be placed into operation as soon as is practicable, and in no event later than eighteen (18) months after a finding of exceedance. This corrective action program will restore the performance of the system of disposal to the original concentration limits established under §192.02(c)(3), to the extent reasonably achievable, and, in any case, as a minimum shall: (a) Conform with the groundwater provisions of § 192.02(c)(3), and (b) Clean up groundwater in conformance with subpart B, modified as appropriate to apply to the disposal site. [60 FR 2866, Jan. 11, 1995] [60 FR 2866, Jan. 11, 1995] Subpart B-Standards for Cleanup of Land and Buildings Contaminated with Residual Radioactive Materials from Inactive Uranium Processing Sites § 192.10 Applicability. This subpart applies to land and buildings that are part of any processing site designated by the Secretary of Energy under section 102 of the Act. section 101 of the Act, states, in part, that "processing site" means— (a) Any site, including the mill, containing residual radioactive materials at which all or substantially all of the uranium was produced for sale to any Federal agency prior to January 1, 1971, under a contract with any Federal agency, except in the case of a site at or near Slick Rock, Colorado, unless (1) Such site was owned or controlled as of Januray 1, 1978, or is thereafter owned or controlled, by any Federal agency, or (2) A license (issued by the (Nuclear Regulatory) Commission or its predecessor agency under the Atomic Energy Act of 1954 or by a State as permitted under section 274 of such Act) for the production at site of any uranium or thorium product derived from ores is in effect on January 1, 1978, or is issued or renewed after such date; and (b) Any other real property or improvement thereon which (1) Is in the vicinity of such site, and (2) Is determined by the Secretary, in consultation with the Commission, to be contaminated with residual radioactive materials derived from such site. |