NR 157.06NR 157.06 Service facility responsibilities. NR 157.06(1)(1) Existing facilities for repair or salvaging of PCBs or products containing PCBs in amounts greater than 2 pounds per unit shall register with the department by January 1, 1978. Any such facility which has failed to register by the required date may not accept for repair or salvaging PCBs or products containing PCBs until such registration has been accomplished. NR 157.06(2)(2) Any facility governed by this subsection shall institute procedures for the safe handling, storage, draining and packaging of PCBs or products containing PCBs for disposal. Except for transformers, containers used for transportation or storage of PCBs or products containing PCBs shall not be used for the storage or transportation of any other material. NR 157.06(3)(a)(a) The service facility shall make provisions with a disposal facility to accept PCBs or products containing PCBs before permitting shipment for disposal. Shipment to a disposal facility in the state of Wisconsin shall be limited to those facilities which meet the requirements of s. NR 157.07. If, for any reason, delivery of the shipment is rejected by the disposal facility, the service facility shall make provisions for immediate return of the shipment or delivery to another disposal facility. NR 157.06(3)(b)(b) The service facility shall make provisions with approved transporters and disposal facilities to complete waste tracking forms provided or approved by the department. A copy of the form shall be retained by the service facility operator for the inspection of the department, and a copy shall be delivered with the PCBs or products containing PCBs to the disposal facility. NR 157.06(4)(4) In lieu of the requirements of sub. (3), the service facility operator may contract with a full service contractor for transport of PCBs or products containing PCBs to the disposal facility. NR 157.06 HistoryHistory: Cr. Register, August, 1977, No. 260, eff. 9-1-77; am. (3) (a), Register, May, 1995, No. 473, eff. 6-1-95. NR 157.07NR 157.07 Disposal methods and facilities. NR 157.07(1)(1) Methods. PCBs or products containing PCBs (liquids, semi-solids) for which a technically and economically feasible incineration method is available for destruction shall be incinerated unless approval for an alternative method of disposal is obtained in writing from the department. Solid or semi-solid products containing PCBs for which a technically and economically feasible incineration method is unavailable shall be disposed of at a landfill facility unless approval for an alternative method of disposal is obtained in writing from the department. NR 157.07(2)(2) Incineration facilities. Facilities for incineration of PCBs or products containing PCBs shall not be established or operated in the state of Wisconsin until written approval of the department is obtained. NR 157.07(2)(a)(a) Complete plans and specifications for an incineration facility shall be submitted to the department in accordance with all applicable provisions of chs. NR 400 to 499 and 660 to 679. NR 157.07(2)(b)(b) Minimum requirements for incineration of PCBs and products containing PCBs include suitable balance of operational parameters (dwell time, temperature, turbulence, and excess oxygen) and a suitable scrubber to remove hydrochloric acid mist from the exhaust gas. Recommended requirements are 2 second dwell time at 1100°C (2000°F) and 3% excess oxygen in the stack gas or 11/2 second dwell time at 1500°C (2700°F) and 2% excess oxygen in the stack gas. NR 157.07(3)(3) Landfill facilities. A landfill for disposal of PCBs and products containing PCBs shall not be established or operated in the state of Wisconsin until written approval of the department is obtained for such disposal as provided in s. NR 660.18 (2) (a). The proposed landfill shall be established and licensed in accordance with the requirements of chs. NR 664, 665 and 670 and other requirements applicable to disposal of PCBs and products containing PCBs. Such a landfill must provide complete long-term protection for the quality of surface and subsurface waters from PCBs deposited therein and must prevent hazards to public health and the environment. Such sites must be located or engineered to avoid direct hydraulic continuity with surface and subsurface waters. Generated leachates must be contained and subsurface flow into the disposal area eliminated. Monitoring wells must be established, and a sampling and analysis program conducted as specified in s. NR 670.403. NR 157.07 NoteNote: Section NR 660.18 (2) (a) no longer exists.
NR 157.07(4)(4) The operator of the incineration or landfill facility shall upon utilization or final disposal of the PCBs or products containing PCBs sign the remaining copies of the waste tracking form, retain a copy and immediately mail a copy to the generator, full-service contractor, or service facility. NR 157.07(5)(5) Facilities recommended for PCB processing and disposal. NR 157.07(5)(a)(a) The department shall maintain a current listing of incinerators and secured landfill sites which are specifically approved by the various state environmental agencies or which may be suitable for disposing of PCBs or products containing PCBs. This list shall provide the names of organizations offering suitable disposal services, including locations and facilities available to any person upon request. However, specific shipping directions, disposal procedures and costs shall be obtained from the organization. NR 157.07(5)(b)(b) The department will consider applications for alternate disposal procedures and alternate disposal sites provided the applicant can demonstrate that the alternatives will not result in environmental pollution. Within 90 days of the receipt of an application for an alternate disposal method or disposal site, the department shall notify the applicant of approval or rejection or shall specify the additional information which is required to determine whether to approve the proposed procedures or sites. NR 157.07 HistoryHistory: Cr. Register, August, 1977, No. 260, eff. 9-1-77; am. (2) (a) and (3) Register, July, 1981, No. 307, eff. 8-1-81; am. (2) (a) and (3), Register, January, 1991, No. 421, eff. 2-1-91; corrections in (2) (a) and (3) made under s. 13.93 (2m) (b) 7., Stats., Register September 2002 No. 561; corrections in (2) (a) and (3) made under s. 13.93 (2m) (b) 7., Stats., Register December 2010 No. 660. NR 157.20NR 157.20 Testing methods for PCBs and products containing PCBs. NR 157.20(1)(1) For transformer fluids, waste oils, insulating liquids, and other non-polar liquids containing PCBs the extraction procedures and analysis methods used shall be any that is appropriate for the material being analyzed, including “Standard Method for Analysis of Polychlorinated Biphenyls in Insulating Liquids by Gas Chromatography,” ASTM standard D 4059-86, American Society for Testing and Materials; “The Determination of Polychlorinated Biphenyls in Transformer Fluid and Waste Oils,” EPA-600/4-81-045, U.S. EPA; EPA Method 3580, EPA Method 3580A, EPA Method 8082, or EPA Method 8082A, all found in “Test Methods for Evaluating Solid Waste,” SW-846, U.S. EPA; and EPA Method 1668A or EPA Method 1668C, U.S. EPA. NR 157.20 NoteNote: Links to the standards listed above can be found on the Wisconsin department of natural resources laboratory accreditation program website and are available for inspection at the offices of the department and the legislative reference bureau.
NR 157.20(2)(2) For paper and paperboard containing PCBs extraction procedures and gas chromatographic analysis shall be used as defined in the“Official Methods of Analysis of the AOAC”, page 285, 15th edition. NR 157.20 NoteNote: This publication may be obtained from the Association of Official Analytical Chemists, 2200 Wilson Blvd., Suite 400-CV, Arlington, VA 22201-3301.
NR 157.20(3)(3) For leachate, non-drinking groundwaters, soils, sediments, and sludges containing PCBs not regulated by a Wisconsin pollution discharge elimination system permit, the extraction procedures and analysis methods used shall be any that is appropriate for the material being analyzed as presented in the “Status Tables for SW-846”; EPA Method 1668A; or EPA Method 1668C. NR 157.20 NoteNote: Links to the standards listed above can be found on the Wisconsin department of natural resources laboratory accreditation program website and are available for inspection at the offices of the department and the legislative reference bureau.
NR 157.20(4)(4) For wastewater and wastewater treatment sludges containing PCBs, testing methods are defined in ch. NR 219. NR 157.20(5)(5) For public drinking waters containing PCBs, testing methods are defined in ch. NR 809. NR 157.20 NoteNote: Copies of the above publications are available for inspection at the offices of the Department of Natural Resources, the Secretary of State, and the Legislative Reference Bureau.
NR 157.20(6)(6) Laboratory test results submitted to the department under this chapter shall be performed by a laboratory certified or registered under ch. NR 149. NR 157.20 HistoryHistory: Cr. Register, August, 1977, No. 260, eff. 9-1-77; cr. (6), Register, April, 1986, No. 364, eff. 8-28-86; r. and recr. Register, November, 1992, No. 443, eff. 12-1-92; correction in (5) made under s. 13.93 (2m) (b) 7., Stats., Register, September, 1995, No. 477; CR 17-046: am. (1), (3) Register February 2021 No. 782, eff. 6-29-21; correction in (1), (3) made under s. 35.17, Stats., Register February 2021 No. 782. NR 157.21NR 157.21 Approval of alternate test procedures. Applications for approval of alternate test procedures for wastewater analysis must be made as directed in s. NR 219.033.
