NR 666.111(3)(e)2.
2. Automatic waste feed cutoff to use if a leak or spill occurs from the direct transfer equipment.
NR 666.111(4)
(4)
Areas where direct transfer vehicles (containers) are located. Applying the definition of container under this section, owners and operators shall comply with all of the following requirements:
NR 666.111(4)(b)
(b) The use and management requirements of subch.
I of ch.
NR 665, except for ss.
NR 665.0170 and
665.0174, and except that in lieu of the special requirements of s.
NR 665.0176 for ignitable or reactive waste, the owner or operator may comply with the requirements for the maintenance of protective distances between the waste management area and any public ways, streets, alleys, or an adjacent property line that can be built upon as required in Tables 2-1 to 2-6 of the National Fire Protection Association's (NFPA) “Flammable and Combustible Liquids Code," (1977 or 1981), incorporated by reference in s.
NR 660.11. The owner or operator shall obtain and keep on file at the facility a written certification by the local fire marshal that the installation meets the subject NFPA codes.
NR 666.111(5)
(5)
Direct transfer equipment. Direct transfer equipment shall meet all of the following requirements:
NR 666.111(5)(a)1.
1. For all new direct transfer equipment, prior to their being put into service.
NR 666.111(5)(a)2.
2. For existing direct transfer equipment within 2 years after August 21, 1991.
NR 666.111(5)(b)
(b) Requirements prior to meeting secondary containment requirements. NR 666.111(5)(b)1.1. For existing direct transfer equipment that does not have secondary containment, the owner or operator shall determine whether the equipment is leaking or is unfit for use. The owner or operator shall obtain and keep on file at the facility a written assessment reviewed and certified by a qualified, registered professional engineer in accordance with s.
NR 670.011 that attests to the equipment's integrity by August 21, 1992.
NR 666.111(5)(b)2.
2. The assessment under subd.
1. shall determine whether the direct transfer equipment is adequately designed and has sufficient structural strength and compatibility with the wastes to be transferred to ensure that it will not collapse, rupture or fail. At a minimum, this assessment shall consider all of the following:
NR 666.111(5)(b)2.a.
a. Design standards, if available, according to which the direct transfer equipment was constructed.
NR 666.111(5)(b)2.d.
d. Documented age of the equipment, if available (otherwise, an estimate of the age).
NR 666.111(5)(b)2.e.
e. Results of a leak test or other integrity examination such that the effects of temperature variations, vapor pockets, cracks, leaks, corrosion and erosion are accounted for.
NR 666.111(5)(b)3.
3. If, as a result of the assessment specified above, the direct transfer equipment is found to be leaking or unfit for use, the owner or operator shall comply with s.
NR 665.0196 (1) and
(2).
NR 666.111(5)(c)1.1. The owner or operator shall inspect at least once each operating hour when hazardous waste is being transferred from the transport vehicle (container) to the boiler or industrial furnace all of the following:
NR 666.111(5)(c)1.a.
a. Overfill or spill control equipment (e.g., waste-feed cutoff systems, bypass systems and drainage systems) to ensure that it is in good working order.
NR 666.111(5)(c)1.b.
b. The above ground portions of the direct transfer equipment to detect corrosion, erosion or releases of waste (e.g., wet spots, dead vegetation).
NR 666.111(5)(c)1.c.
c. Data gathered from monitoring equipment and leak-detection equipment, (e.g., pressure and temperature gauges) to ensure that the direct transfer equipment is being operated according to its design.
NR 666.111(5)(c)2.
2. The owner or operator shall inspect cathodic protection systems, if used, to ensure that they are functioning properly according to the schedule provided by s.
NR 665.0195 (2).
NR 666.111(5)(c)3.
3. Records of inspections made under this paragraph shall be maintained in the operating record at the facility, and available for inspection for at least 3 years from the date of the inspection.
NR 666.111 History
History: CR 05-032: cr.
Register July 2006 No. 607, eff. 8-1-06.
NR 666.112
NR 666.112 Regulation of residues. A residue derived from the burning or processing of hazardous waste in a boiler or industrial furnace is not excluded from the definition of a hazardous waste under s.
NR 661.0004 (2) (d),
(g) or
(h) unless the device and the owner or operator meet all of the following requirements:
NR 666.112(1)(a)
(a) Boilers. Boilers shall burn at least 50% coal on a total heat input or mass input basis, whichever results in the greater mass feed rate of coal.
NR 666.112(1)(c)
(c)
Cement kilns. Cement kilns shall process at least 50% by weight normal cement-production raw materials.
NR 666.112(2)
(2) The owner or operator demonstrates that the hazardous waste does not significantly affect the residue by demonstrating conformance with either of the following criteria:
NR 666.112(2)(a)
(a) Comparison of waste-derived residue with normal residue. The waste-derived residue may not contain ch.
NR 661 Appendix VIII constituents (toxic constituents) that could reasonably be attributable to the hazardous waste at concentrations significantly higher than in residue generated without burning or processing of hazardous waste, using the following procedure. Toxic compounds that could reasonably be attributable to burning or processing the hazardous waste (constituents of concern) include toxic constituents in the hazardous waste, and the organic compounds listed in ch.
NR 661 Appendix VIII that may be generated as products of incomplete combustion. For polychlorinated dibenzo-p-dioxins and polychlorinated dibenzo-furans, analyses shall be performed to determine specific congeners and homologues, and the results converted to 2,3,7,8-TCDD equivalent values using the procedure specified in section 4.0 of ch.
NR 666 Appendix IX.
NR 666.112(2)(a)1.
1. `Normal residue.' Concentrations of toxic constituents of concern in normal residue shall be determined based on analyses of a minimum of 10 samples representing a minimum of 10 days of operation. Composite samples may be used to develop a sample for analysis if the compositing period does not exceed 24 hours. The upper tolerance limit (at 95% confidence with a 95% proportion of the sample distribution) of the concentration in the normal residue shall be considered the statistically-derived concentration in the normal residue. If changes in raw materials or fuels reduce the statistically-derived concentrations of the toxic constituents of concern in the normal residue, the statistically-derived concentrations shall be revised or statistically-derived concentrations of toxic constituents in normal residue shall be established for a new mode of operation with the new raw material or fuel. To determine the upper tolerance limit in the normal residue, the owner or operator shall use statistical procedures prescribed in “Statistical Methodology for Bevill Residue Determinations" in ch.
NR 666 Appendix IX .
NR 666.112(2)(a)2.
2. `Waste-derived residue.' Waste-derived residue shall be sampled and analyzed as often as necessary to determine whether the residue generated during each 24-hour period has concentrations of toxic constituents that are higher than the concentrations established for the normal residue under subd.
1. If so, hazardous waste burning has significantly affected the residue and the residue may not be excluded from the definition of a hazardous waste. Concentrations of toxic constituents of concern in the waste-derived residue shall be determined based on analysis of one or more samples obtained over a 24-hour period. Multiple samples may be analyzed, and multiple samples may be taken to form a composite sample for analysis if the sampling period does not exceed 24 hours. If more than one sample is analyzed to characterize waste-derived residues generated over a 24-hour period, the concentration of each toxic constituent shall be the arithmetic mean of the concentrations in the samples. No results may be disregarded.
NR 666.112(2)(b)
(b) Comparison of waste-derived residue concentrations with health-based limits. NR 666.112(2)(b)1.1. `Nonmetal constituents.' The concentration of each nonmetal toxic constituent of concern (specified in par.
(a)) in the waste-derived residue may not exceed the health-based level specified in ch.
NR 666 Appendix VII, or the level of detection, whichever is higher. If a health-based limit for a constituent of concern is not listed in ch.
NR 666 Appendix VII, then a limit of 0.002 micrograms per kilogram or the level of detection (which shall be determined using appropriate analytical methods), whichever is higher, shall be used. The levels specified in ch.
NR 666 Appendix VII (and the default level of 0.002 micrograms per kilogram or the level of detection for constituents as identified in Note 1 of ch.
NR 666 Appendix VII) are administratively stayed under the condition, for those constituents specified in par.
(a), that the owner or operator complies with alternative levels defined as the land disposal restriction limits specified in s.
NR 668.43 for F039 nonwastewaters. In complying with those alternative levels, if an owner or operator is unable to detect a constituent despite documenting use of best good-faith efforts as defined by applicable department guidance or standards, the owner or operator is deemed to be in compliance for that constituent. Until new guidance or standards are developed, the owner or operator may demonstrate such good faith efforts by achieving a detection limit for the constituent that does not exceed an order of magnitude above the level provided by s.
NR 668.43 for F039 nonwastewaters. In complying with the s.
NR 668.43 F039 nonwastewater levels for polychlorinated dibenzo-p-dioxins and polychlorinated dibenzo-furans, analyses shall be performed for total hexachlorodibenzo-p-dioxins, total hexachlorodibenzofurans, total pentachlorodibenzo-p-dioxins, total pentachlorodibenzofurans, total tetrachlorodibenzo-p-dioxins and total tetrachlorodibenzofurans.
NR 666.112 Note
Note: The administrative stay, under the condition that the owner or operator complies with alternative levels defined as the land disposal restriction limits specified in s.
NR 668.43 for F039 nonwastewaters, remains in effect until further administrative action is taken and notice is published in the federal register and the Code of Federal Regulations.
NR 666.112(2)(b)3.
3. `Sampling and analysis.' Waste-derived residue shall be sampled and analyzed as often as necessary to determine whether the residue generated during each 24-hour period has concentrations of toxic constituents that are higher than the health-based levels. Concentrations of toxic constituents of concern in the waste-derived residue shall be determined based on analysis of one or more samples obtained over a 24-hour period. Multiple samples may be analyzed, and multiple samples may be taken to form a composite sample for analysis if the sampling period does not exceed 24 hours. If more than one sample is analyzed to characterize waste-derived residues generated over a 24-hour period, the concentration of each toxic constituent shall be the arithmetic mean of the concentrations in the samples. No results may be disregarded.
NR 666.112(3)
(3) Records sufficient to document compliance with this section shall be retained until closure of the boiler or industrial furnace unit. At a minimum, all of the following shall be recorded:
NR 666.112(3)(b)
(b) If the waste-derived residue is compared with normal residue under sub.
(2) (a), both of the following:
NR 666.112(3)(b)2.
2. Data and information, including analyses of samples as necessary, obtained to determine if changes in raw materials or fuels would reduce the concentration of toxic constituents of concern in the normal residue.
NR 666.112 History
History: CR 05-032: cr.
Register July 2006 No. 607, eff. 8-1-06; corrections in (2) (a) (intro.), 1., (2) (b) 1., 2. made under s.
13.92 (4) (b) 7., Stats.,
Register March 2013 No. 687;
CR 16-007: am. (2) (a) (intro.), (b) 1.
Register July 2017 No. 739, eff. 8-1-17;
CR 19-082: am. (1) (b), (2) (b) 2.
Register August 2020 No. 776, eff. 9-1-20; correction in (2) (b) 2. made under s.
35.17, Stats.,
Register August 2020 No. 776; correction in (intro.) made under s.
13.92 (4) (b) 7., Stats.,
Register April 2021 No. 784.
NR 666.200(1)(1)
This subchapter identifies when military munitions become a solid waste, and, if these wastes are also hazardous under this subchapter or ch.
NR 661, the management standards that apply to these wastes.
NR 666.200(2)
(2) Unless otherwise specified in this subchapter, all applicable requirements in chs.
NR 660 to
670 apply to waste military munitions.
NR 666.200 History
History: CR 05-032: cr.
Register July 2006 No. 607, eff. 8-1-06.
NR 666.201
NR 666.201 Definitions. The following definitions apply to this subchapter:
NR 666.201(1)
(1) “Active range" means a military range that is currently in service and is being regularly used for range activities.
NR 666.201(2)
(2) “Chemical agent and munition" means an agent or munition that, through its chemical properties, produces lethal or other damaging effects on human beings, except that the term does not include riot control agents, chemical herbicides, smoke and other obscuration materials.
NR 666.201(3)
(3) “DDESB" means the United States department of defense explosives safety board.
NR 666.201(4)
(4) “Inactive range" means a military range that is not currently being used, but that is still under military control and considered by the military to be a potential range area, and that has not been put to a new use that is incompatible with range activities.
NR 666.201(5)
(5) “Military" means the U.S. department of defense (DOD), U.S. armed services, U.S. coast guard, national guard, U.S. department of energy (DOE), or other parties under contract or acting as an agent for any of them, who handle military munitions.
NR 666.201(6)
(6) “Military range" means designated land and water areas set aside, managed and used to conduct research on, develop, test and evaluate military munitions and explosives, other ordnance or weapon systems, or to train military personnel in their use and handling. Ranges include firing lines and positions, maneuver areas, firing lanes, test pads, detonation pads, impact areas and buffer zones with restricted access and exclusionary areas.
NR 666.201(7)
(7) “Unexploded ordnance" or “UXO" means military munitions that have been primed, fused, armed or otherwise prepared for action, and have been fired, dropped, launched, projected or placed in such a manner as to constitute a hazard to operations, installation, personnel or material and remain unexploded either by malfunction, design or any other cause.
NR 666.201 History
History: CR 05-032: cr.
Register July 2006 No. 607, eff. 8-1-06.
NR 666.202(1)(1)
A military munition is not a solid waste when either of the following occurs:
NR 666.202(1)(a)
(a) It is used for its intended purpose, including any of the following:
NR 666.202(1)(a)1.
1. Use in training military personnel or explosives and munitions emergency response specialists (including training in proper destruction of unused propellant or other munitions).
NR 666.202(1)(a)2.
2. Use in research, development, testing and evaluation of military munitions, weapons or weapon systems.
NR 666.202(1)(a)3.
3. Recovery, collection and on-range destruction of unexploded ordnance and munitions fragments during range clearance activities at active or inactive ranges. However, “use for intended purpose" does not include the on-range disposal or burial of unexploded ordnance and contaminants when the burial is not a result of product use.
NR 666.202(1)(b)
(b) It is an unused munition, or component thereof, which is being repaired, reused, recycled, reclaimed, disassembled, reconfigured or otherwise subjected to materials recovery activities, unless the activities involve use constituting disposal as defined in s.
NR 661.0002 (3) (a), or burning for energy recovery as defined in s.
NR 661.0002 (3) (b).
NR 666.202(2)
(2) An unused military munition is a solid waste when any of the following occurs:
NR 666.202(2)(a)
(a) The munition is abandoned by being disposed of, burned, detonated (except during intended use as specified in sub.
(1)), incinerated or treated prior to disposal.
NR 666.202(2)(b)
(b) The munition is removed from storage in a military magazine or other storage area for the purpose of being disposed of, burned, incinerated or treated prior to disposal.
NR 666.202(2)(c)
(c) The munition is deteriorated or damaged (e.g., the integrity of the munition is compromised by cracks, leaks or other damage) to the point that it cannot be put into serviceable condition, and cannot reasonably be recycled or used for other purposes.
NR 666.202(2)(d)
(d) The munition has been declared a solid waste by an authorized military official.
NR 666.202(3)
(3) A used or fired military munition is a solid waste when either of the following occurs:
NR 666.202(3)(a)
(a) When it is transported off range or from the site of use, where the site of use is not a range, for the purposes of storage, reclamation, treatment, disposal or treatment prior to disposal.
NR 666.202(3)(b)
(b) If it is recovered, collected and then disposed of by burial, or landfilling either on or off a range.
NR 666.202(4)
(4) For purposes of s.
289.01 (33), Stats., a used or fired military munition is a solid waste, and, therefore, is potentially subject to corrective action authorities under ss.
291.37,
291.95 and
291.97, Stats.,
42 USC 6924 (u) and (v) and 6928
(h), and subch.
S of ch. NR 664, or imminent danger authorities under s.
291.85, Stats., or
42 USC 6973 (a), if the munition lands off-range and is not promptly rendered safe or retrieved. Any imminent danger threats associated with any remaining material shall be addressed. If remedial action is infeasible, the operator of the range shall maintain a record of the event for as long as any threat remains. The record shall include the type of munition and its location to the extent the location is known
.
NR 666.202 History
History: CR 05-032: cr.
Register July 2006 No. 607, eff. 8-1-06;
CR 19-082: am. (1) (b), (4)
Register August 2020 No. 776, eff. 9-1-20.
NR 666.203
NR 666.203 Standards applicable to the transportation of solid waste military munitions. NR 666.203(1)(1)
Criteria for hazardous waste regulation of waste non-chemical military munitions in transportation. NR 666.203(1)(a)
(a) Waste military munitions that are being transported and that exhibit a hazardous waste characteristic or are listed as hazardous waste under ch.
NR 661, are subject to chs.
NR 660 to
670, unless all the following conditions are met:
NR 666.203(1)(a)1.
1. The waste military munitions are not chemical agents or chemical munitions.
NR 666.203(1)(a)2.
2. The waste military munitions are transported in accordance with the U.S. department of defense shipping controls applicable to the transport of military munitions.
NR 666.203(1)(a)3.
3. The waste military munitions are transported from a military owned or operated installation to a military owned or operated treatment, storage or disposal facility.
NR 666.203(1)(a)4.
4. The transporter of the waste provides oral notice to the department within 24 hours from the time the transporter becomes aware of any loss or theft of the waste military munitions, or any failure to meet a condition of this paragraph that may endanger health or the environment. In addition, a written submission describing the circumstances shall be provided within 5 days from the time the transporter becomes aware of any loss or theft of the waste military munitions or any failure to meet a condition of this paragraph.
NR 666.203(1)(b)
(b) If any waste military munitions shipped under par.
(a) are not received by the receiving facility within 45 days of the day the waste was shipped, the owner or operator of the receiving facility shall report this non-receipt to the department within 5 days.
NR 666.203(1)(c)
(c) The exemption in par.
(a) from regulation as hazardous waste shall apply only to the transportation of non-chemical waste military munitions. It does not affect the regulatory status of waste military munitions as hazardous wastes with regard to storage, treatment or disposal.
