reglab/statecodes huggingface dataset:
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter K - Surface Impoundments › Section NR 664.0229 - Special requirements for ignitable or reactive waste

Current through June 24, 2024
Ignitable or reactive waste may not be placed in a surface
					 impoundment, unless the waste and impoundment satisfy all applicable
					 requirements of ch. NR 668, and sub. (1), (2) or (3):
(1) The waste is treated, rendered or mixed
				  before or immediately after placement in the impoundment so that both of the
				  following apply:
(a) The resulting waste,
				  mixture or dissolution of material no longer meets the definition of ignitable
				  or reactive waste under s. NR 661.0021 or 661.0023.
(b) Section
				  NR
				  664.0017(2) is complied
				  with.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter K - Surface Impoundments › Section NR 664.0230 - Special requirements for incompatible wastes

Current through June 24, 2024
Incompatible wastes, or incompatible wastes and materials,
					 (see ch. NR 664 Appendix V for examples) may not be placed in the same surface
					 impoundment, unless s.
					 NR
					 664.0017(2) is complied
					 with.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter K - Surface Impoundments › Section NR 664.0231 - Special requirements for hazardous wastes F020, F021, F022, F023, F026 and F027

Current through June 24, 2024
(1) Hazardous wastes F020, F021, F022, F023,
				  F026 and F027 may not be placed in a surface impoundment unless the owner or
				  operator operates the surface impoundment in accordance with a management plan
				  for these wastes that is approved by the department pursuant to the standards
				  set out in this subsection, and in accord with all other applicable
				  requirements of this chapter. All of the following factors shall be considered:
(a) The volume and physical and chemical
				  characteristics of the wastes, including their potential to migrate through
				  soil or to volatilize or escape into the atmosphere.
(b) The attenuative properties of underlying
				  and surrounding soils or other materials.
(c) The mobilizing properties of other
				  materials co-disposed with these wastes.
(d) The effectiveness of additional
				  treatment, design or monitoring techniques.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter K - Surface Impoundments › Section NR 664.0232 - Air emission standards

Current through June 24, 2024
The owner or operator shall manage all hazardous waste
					 placed in a surface impoundment in accordance with the applicable requirements
					 of subchs. BB and CC.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0250 - Applicability

Current through June 24, 2024
(1) This subchapter applies to owners and
				  operators of facilities that store or treat hazardous waste in piles, except as
				  s.
				  NR
				  664.0001 provides otherwise.
(2) This subchapter does not apply to owners
				  or operators of waste piles that are closed with wastes left in place. Those
				  waste piles are regulated under subch. N (landfills).
(3) The owner or operator of any waste pile
				  that is inside or under a structure that provides protection from precipitation
				  so that neither run-off nor leachate is generated is not regulated under s.
				  NR
				  664.0251 or under subch. F, if all of the following
				  are met:
(a) Liquids or materials containing
				  free liquids are not placed in the pile.
(b) The pile is protected from surface water
				  run-on by the structure or in some other manner.
(c) The pile is designed and operated to
				  control dispersal of the waste by wind, where necessary, by means other than
				  wetting.
(d) The pile will not
				  generate leachate through decomposition or other reactions.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0251 - Design and operating requirements

Current through June 24, 2024
(1) A waste pile
				  (except for an existing portion of a waste pile) shall have both of the
				  following:
(a) A liner that is designed,
				  constructed and installed to prevent any migration of wastes out of the pile
				  into the adjacent subsurface soil or groundwater or surface water at any time
				  during the active life (including the closure period) of the waste pile. The
				  liner may be constructed of materials that may allow waste to migrate into the
				  liner itself (but not into the adjacent subsurface soil or groundwater or
				  surface water) during the active life of the facility. The liner shall be all
				  of the following:
1. Constructed of materials
				  that have appropriate chemical properties and sufficient strength and thickness
				  to prevent failure due to pressure gradients (including static head and
				  external hydrogeologic forces), physical contact with the waste or leachate to
				  which they are exposed, climatic conditions, the stress of installation and the
				  stress of daily operation.
2.
				  Placed upon a foundation or base capable of providing support to the liner and
				  resistance to pressure gradients above and below the liner to prevent failure
				  of the liner due to settlement, compression or uplift.
3. Installed to cover all surrounding earth
				  likely to be in contact with the waste or leachate.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0252 - Action leakage rate

Current through June 24, 2024
(1) The department shall approve an action
				  leakage rate for waste pile units subject to s.
				  NR 664.0251(3)
				  or (4). The action leakage rate is the
				  maximum design flow rate that the leak detection system can remove without the
				  fluid head on the bottom liner exceeding one foot. The action leakage rate
				  shall include an adequate safety margin to allow for uncertainties in the
				  design (e.g., slope, hydraulic conductivity, thickness of drainage material),
				  construction, operation and location of the leak detection system, waste and
				  leachate characteristics, likelihood and amounts of other sources of liquids in
				  the leak detection system and proposed response actions (e.g., the action
				  leakage rate shall consider decreases in the flow capacity of the system over
				  time resulting from siltation and clogging, rib layover and creep of synthetic
				  components of the system, overburden pressures, etc.).
(2) To determine if the action leakage rate
				  has been exceeded, the owner or operator shall convert the weekly flow rate
				  from the monitoring data obtained under s.
				  NR
				  664.0254(3), to an average daily flow
				  rate (gallons per acre per day) for each sump. Unless the department approves a
				  different calculation, the average daily flow rate for each sump shall be
				  calculated weekly during the active life and closure period.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0253 - Response actions

Current through June 24, 2024
(1) The owner or operator of waste pile units
				  subject to s.
				  NR 664.0251(3)
				  or (4) shall have an approved response action
				  plan before receipt of waste. The response action plan shall set forth the
				  actions to be taken if the action leakage rate has been exceeded. At a minimum,
				  the response action plan shall describe the actions specified in sub.
				  (2).
(2) If the flow rate into the
				  leak detection system exceeds the action leakage rate for any sump, the owner
				  or operator shall do all of the following:
(a) Notify the department in writing of the
				  exceedance within 7 days of the determination.
(b) Submit a preliminary written assessment
				  to the department within 14 days of the determination, as to the amount of
				  liquids, likely sources of liquids, possible location, size and cause of any
				  leaks and short-term actions taken and planned.
(c) Determine to the extent practicable the
				  location, size and cause of any leak.
(d) Determine whether waste receipt should
				  cease or be curtailed, whether any waste should be removed from the unit for
				  inspection, repairs or controls and whether or not the unit should be
				  closed.
(e) Determine any other
				  short-term and long-term actions to be taken to mitigate or stop any
				  leaks.
(f) Within 30 days after the
				  notification that the action leakage rate has been exceeded, submit to the
				  department the results of the analyses specified in pars. (c), (d) and (e), the
				  results of actions taken and actions planned. Monthly thereafter, as long as
				  the flow rate in the leak detection system exceeds the action leakage rate, the
				  owner or operator shall submit to the department a report summarizing the
				  results of any remedial actions taken and actions planned.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0254 - Monitoring and inspection

Current through June 24, 2024
(1) During
				  construction or installation, liners (except in the case of existing portions
				  of piles exempt from s.
				  NR
				  664.0251(1) ) and cover systems
				  (e.g., membranes, sheets or coatings) shall be inspected for uniformity, damage
				  and imperfections (e.g., holes, cracks, thin spots or foreign materials). Both
				  of the following inspections are required immediately after construction or
				  installation:
(a) Synthetic liners and covers
				  shall be inspected to ensure tight seams and joints and the absence of tears,
				  punctures or blisters.
(b)
				  Soil-based and admixed liners and covers shall be inspected for imperfections
				  including lenses, cracks, channels, root holes or other structural
				  non-uniformities that may cause an increase in the permeability of the liner or
				  cover.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0256 - Special requirements for ignitable or reactive waste

Current through June 24, 2024
Ignitable or reactive waste may not be placed in a waste
					 pile unless the waste and waste pile satisfy all applicable requirements of ch.
					 NR 668 and sub. (1) or (2):
(1) The
				  waste is treated, rendered or mixed before or immediately after placement in
				  the pile so that both of the following apply:
(a) The resulting waste, mixture or
				  dissolution of material no longer meets the definition of ignitable or reactive
				  waste under s. NR 661.0021 or 661.0023.
(b) Section
				  NR
				  664.0017(2)  is complied
				  with.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0257 - Special requirements for incompatible wastes

Current through June 24, 2024
(1) Incompatible
				  wastes, or incompatible wastes and materials, (see ch. NR 664 Appendix V for
				  examples) may not be placed in the same pile, unless s.
				  NR
				  664.0017(2) is complied
				  with.
(2) A pile of hazardous waste
				  that is incompatible with any waste or other material stored nearby in
				  containers, other piles, open tanks or surface impoundments shall be separated
				  from the other materials, or protected from them by means of a dike, berm, wall
				  or other device.
(3) Hazardous
				  waste may not be piled on the same base where incompatible wastes or materials
				  were previously piled, unless the base has been decontaminated sufficiently to
				  ensure compliance with s.
				  NR
				  664.0017(2).
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0258 - Closure and long-term care

Current through June 24, 2024
(1) At closure, the
				  owner or operator shall remove or decontaminate all waste residues,
				  contaminated containment system components (liners, etc.), contaminated
				  subsoils and structures and equipment contaminated with waste and leachate, and
				  manage them as hazardous waste unless s. NR 661.0003(4) applies.
(2) If, after removing or decontaminating all
				  residues and making all reasonable efforts to effect removal or decontamination
				  of contaminated components, subsoils, structures and equipment as required in
				  sub. (1), the owner or operator finds that not all contaminated subsoils can be
				  practicably removed or decontaminated, the owner or operator shall close the
				  facility and perform long-term care in accordance with the closure and
				  long-term care requirements that apply to landfills (s.
				  NR
				  664.0310 ).
(3)
(a) The
				  owner or operator of a waste pile that does not comply with the liner
				  requirements of s.
				  NR 664.0251(1)
				  (a) and is not exempt from them in accordance
				  with s.
				  NR
				  664.0250(3) or 664.0251(2), shall do
				  both of the following:
1. Include in the
				  closure plan for the pile under s.
				  NR
				  664.0112 both a plan for complying with sub. (1) and a
				  contingent plan for complying with sub. (2) in case not all contaminated
				  subsoils can be practicably removed at closure.
2. Prepare a contingent long-term care plan
				  under s.
				  NR
				  664.0118 for complying with sub. (2) in case not all
				  contaminated subsoils can be practicably removed at
				  closure.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter L - Waste Piles › Section NR 664.0259 - Special requirements for hazardous wastes F020, F021, F022, F023, F026 and F027

Current through June 24, 2024
(1) Hazardous wastes F020, F021, F022, F023,
				  F026 and F027 may not be placed in waste piles that are not enclosed (as
				  defined in s.
				  NR
				  664.0250(3) ) unless the owner or
				  operator operates the waste pile in accordance with a management plan for these
				  wastes that is approved by the department pursuant to the standards set out in
				  this subsection, and in accord with all other applicable requirements of this
				  chapter. All of the following factors shall be considered:
(a) The volume and physical and chemical
				  characteristics of the wastes, including their potential to migrate through
				  soil or to volatilize or escape into the atmosphere.
(b) The attenuative properties of underlying
				  and surrounding soils or other materials.
(c) The mobilizing properties of other
				  materials co-disposed with these wastes.
(d) The effectiveness of additional
				  treatment, design or monitoring techniques.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter M - Land Treatment › Section NR 664.0270 - Applicability

Current through June 24, 2024
Land treatment of any hazardous waste is prohibited. The
					 department may not grant a variance under s.
					 291.31, Stats., to allow
					 land treatment of any hazardous waste, as identified or listed in ch. NR
					 661.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0300 - Applicability

Current through June 24, 2024
This subchapter applies to owners and operators of
					 facilities that dispose of hazardous waste in landfills, except as s.
					 NR
					 664.0001 provides otherwise.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0301 - Design and operating requirements

Current through June 24, 2024
(1) Any landfill
				  that is not covered by sub. (3) or s.
				  NR
				  665.0301(1) shall have a liner system
				  for all portions of the landfill (except for existing portions of the
				  landfill). The liner system shall have both of the following:
(a) A liner that is designed, constructed and
				  installed to prevent any migration of wastes out of the landfill to the
				  adjacent subsurface soil or groundwater or surface water at any time during the
				  active life (including the closure period) of the landfill. The liner shall be
				  constructed of materials that prevent wastes from passing into the liner during
				  the active life of the facility. The liner shall be all of the following:
1. Constructed of materials that have
				  appropriate chemical properties and sufficient strength and thickness to
				  prevent failure due to pressure gradients (including static head and external
				  hydrogeologic forces), physical contact with the waste or leachate to which
				  they are exposed, climatic conditions, the stress of installation and the
				  stress of daily operation.
2.
				  Placed upon a foundation or base capable of providing support to the liner and
				  resistance to pressure gradients above and below the liner to prevent failure
				  of the liner due to settlement, compression or uplift.
3. Installed to cover all surrounding earth
				  likely to be in contact with the waste or leachate.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0302 - Action leakage rate

Current through June 24, 2024
(1) The department shall approve an action
				  leakage rate for landfill units subject to s.
				  NR 664.0301(3)
				  or (4). The action leakage rate is the
				  maximum design flow rate that the leak detection system can remove without the
				  fluid head on the bottom liner exceeding one foot. The action leakage rate
				  shall include an adequate safety margin to allow for uncertainties in the
				  design (e.g., slope, hydraulic conductivity, thickness of drainage material),
				  construction, operation and location of the leak detection system, waste and
				  leachate characteristics, likelihood and amounts of other sources of liquids in
				  the leak detection system and proposed response actions (e.g., the action
				  leakage rate shall consider decreases in the flow capacity of the system over
				  time resulting from siltation and clogging, rib layover and creep of synthetic
				  components of the system, overburden pressures, etc.).
(2) To determine if the action leakage rate
				  has been exceeded, the owner or operator shall convert the weekly or monthly
				  flow rate from the monitoring data obtained under s.
				  NR
				  664.0303(3), to an average daily flow
				  rate (gallons per acre per day) for each sump. Unless the department approves a
				  different calculation, the average daily flow rate for each sump shall be
				  calculated weekly during the active life and closure period, and monthly during
				  the long-term care period when monthly monitoring is required under s.
				  NR
				  664.0303(3).
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0303 - Monitoring and inspection

Current through June 24, 2024
(1) During
				  construction or installation, liners (except in the case of existing portions
				  of landfills exempt from s.
				  NR
				  664.0301(1) ) and cover systems
				  (e.g., membranes, sheets or coatings) shall be inspected for uniformity, damage
				  and imperfections (e.g., holes, cracks, thin spots or foreign materials). Both
				  of the following inspections are required immediately after construction or
				  installation:
(a) Synthetic liners and covers
				  shall be inspected to ensure tight seams and joints and the absence of tears,
				  punctures or blisters.
(b)
				  Soil-based and admixed liners and covers shall be inspected for imperfections
				  including lenses, cracks, channels, root holes or other structural
				  non-uniformities that may cause an increase in the permeability of the liner or
				  cover.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0304 - Response actions

Current through June 24, 2024
(1) The owner or operator of landfill units
				  subject to s.
				  NR 664.0301(3)
				  or (4) shall have an approved response action
				  plan before receipt of waste. The response action plan shall set forth the
				  actions to be taken if the action leakage rate has been exceeded. At a minimum,
				  the response action plan shall describe the actions specified in sub.
				  (2).
(2) If the flow rate into the
				  leak detection system exceeds the action leakage rate for any sump, the owner
				  or operator shall do all of the following:
(a) Notify the department in writing of the
				  exceedence within 7 days of the determination.
(b) Submit a preliminary written assessment
				  to the department within 14 days of the determination, as to the amount of
				  liquids, likely sources of liquids, possible location, size and cause of any
				  leaks and short-term actions taken and planned.
(c) Determine to the extent practicable the
				  location, size and cause of any leak.
(d) Determine whether waste receipt should
				  cease or be curtailed, whether any waste should be removed from the unit for
				  inspection, repairs or controls and whether or not the unit should be
				  closed.
(e) Determine any other
				  short-term and longer-term actions to be taken to mitigate or stop any
				  leaks.
(f) Within 30 days after the
				  notification that the action leakage rate has been exceeded, submit to the
				  department the results of the analyses specified pars. (c), (d) and (e), the
				  results of actions taken and actions planned. Monthly thereafter, as long as
				  the flow rate in the leak detection system exceeds the action leakage rate, the
				  owner or operator shall submit to the department a report summarizing the
				  results of any remedial actions taken and actions planned.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0309 - Surveying and recordkeeping

Current through June 24, 2024
The owner or operator of a landfill shall maintain both of
					 the following items in the operating record required under s.
					 NR
					 664.0073:
(1)
				  On a map, the exact location and dimensions, including depth, of each cell with
				  respect to permanently surveyed benchmarks.
(2) The contents of each cell and the
				  approximate location of each hazardous waste type within each cell.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0310 - Closure and long-term care

Current through June 24, 2024
(1) At final
				  closure of the landfill or upon closure of any cell, the owner or operator
				  shall cover the landfill or cell with a final cover designed and constructed to
				  do all of the following:
(a) Provide
				  long-term minimization of migration of liquids through the closed
				  landfill.
(b) Function with minimum
				  maintenance.
(c) Promote drainage
				  and minimize erosion or abrasion of the cover.
(d) Accommodate settling and subsidence so
				  that the cover's integrity is maintained.
(e) Have a permeability less than or equal to
				  the permeability of any bottom liner system or natural subsoils
				  present.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0312 - Special requirements for ignitable or reactive waste

Current through June 24, 2024
(1) Except as
				  provided in sub. (2), and in s.
				  NR
				  664.0316, ignitable or reactive waste may not be
				  placed in a landfill, unless the waste and landfill meet all applicable
				  requirements of ch. NR 668 and both of the following:
(a) The resulting waste, mixture or
				  dissolution of material no longer meets the definition of ignitable or reactive
				  waste under s. NR 661.0021 or 661.0023.
(b) Section
				  NR
				  664.0017(2) is complied
				  with.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0313 - Special requirements for incompatible wastes

Current through June 24, 2024
Incompatible wastes, or incompatible wastes and materials,
					 (see ch. NR 664 Appendix V for examples) may not be placed in the same landfill
					 cell, unless s.
					 NR
					 664.0017(2) is complied
					 with.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0314 - Special requirements for bulk and containerized liquids

Current through June 24, 2024
(1) The placement
				  of bulk or non-containerized liquid hazardous waste or hazardous waste
				  containing free liquids (whether or not sorbents have been added) in any
				  landfill is prohibited.
(2) To
				  demonstrate the absence or presence of free liquids in either a containerized
				  or a bulk waste, the following test shall be used: Method 9095B (paint filter
				  liquids test) as described in "Test Methods for Evaluating Solid Waste,
				  Physical/Chemical Methods," EPA SW-846, incorporated by reference in s.
				  NR
				  660.11.
(3) Containers holding free liquids may not
				  be placed in a landfill unless par. (a), (b), (c) or (d) applies:
(a) All free-standing liquid is handled in
				  one of the following ways:
1. It has been
				  removed by decanting, or other methods.
2. It has been mixed with sorbent or
				  solidified so that free-standing liquid is no longer observed.
3. It has been otherwise
				  eliminated.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0315 - Special requirements for containers

Current through June 24, 2024
Unless they are very small, such as an ampule, containers
					 shall be either of the following:
(1)
				  At least 90% full when placed in the landfill.
(2) Crushed, shredded or similarly reduced in
				  volume to the maximum practical extent before burial in the landfill.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0316 - Disposal of small containers of hazardous waste in overpacked drums (lab packs)

Current through June 24, 2024
Small containers of hazardous waste in overpacked drums
					 (lab packs) may be placed in a landfill if all of the following requirements
					 are met:
(1) Hazardous waste shall be
				  packaged in non-leaking inside containers. The inside containers shall be of a
				  design and constructed of a material that will not react dangerously with, be
				  decomposed by or be ignited by the contained waste. Inside containers shall be
				  tightly and securely sealed. The inside containers shall be of the size and
				  type specified in the U.S. department of transportation (DOT) hazardous
				  materials regulations (49 CFR parts 173, 178 and 179), if those regulations
				  specify a particular inside container for the waste.
(2) The inside containers shall be overpacked
				  in an open head DOT-specification metal shipping container (49 CFR parts 178
				  and 179) of no more than 416-liter (110 gallon) capacity and surrounded by, at
				  a minimum, a sufficient quantity of sorbent material, determined to be
				  nonbiodegradable in accordance with s.
				  NR
				  664.0314(4), to completely sorb all
				  of the liquid contents of the inside containers. The metal outer container
				  shall be full after it has been packed with inside containers and sorbent
				  material.
(3) The sorbent material
				  used may not be capable of reacting dangerously with, being decomposed by or
				  being ignited by the contents of the inside containers, in accordance with s.
				  NR
				  664.0017(2).
(4) Incompatible wastes, as defined in s.
				  NR
				  660.10, may not be placed in the same outside
				  container.
(5) Reactive wastes,
				  other than cyanide- or sulfide-bearing waste as defined in s. NR 661.0023(1)
				  (e), shall be treated or rendered non-reactive prior to packaging in accordance
				  with subs. (1) to (4). Cyanide- and sulfide-bearing reactive waste may be
				  packed in accordance with subs. (1) to (4) without first being treated or
				  rendered non-reactive.
(6) The
				  disposal is in compliance with the requirements of ch. NR 668. Persons who
				  incinerate lab packs according to the requirements in s.
				  NR
				  668.42(3) (a) may use fiber drums in
				  place of metal outer containers. The fiber drums shall meet the DOT
				  specifications in
				  49 CFR
				  173.12 and be overpacked according to the
				  requirements in sub. (2).
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter N - Landfills › Section NR 664.0317 - Special requirements for hazardous wastes F020, F021, F022, F023, F026 and F027

Current through June 24, 2024
(1) Hazardous wastes F020, F021, F022, F023,
				  F026 and F027 may not be placed in a landfill unless the owner or operator
				  operates the landfill in accord with a management plan for these wastes that is
				  approved by the department pursuant to the standards set out in this
				  subsection, and in accord with all other applicable requirements of this
				  chapter. All of the following factors shall be considered:
(a) The volume and physical and chemical
				  characteristics of the wastes, including their potential to migrate through the
				  soil or to volatilize or escape into the atmosphere.
(b) The attenuative properties of underlying
				  and surrounding soils or other materials.
(c) The mobilizing properties of other
				  materials co-disposed with these wastes.
(d) The effectiveness of additional
				  treatment, design or monitoring requirements.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0340 - Applicability

Current through June 24, 2024
(1) This subchapter applies to owners and
				  operators of hazardous waste incinerators (as defined in s.
				  NR
				  660.10 ), except as s.
				  NR
				  664.0001 provides otherwise.
(2)
(a)
				  Except as provided by pars. (b) to (d), the standards of this subchapter do not
				  apply to a new hazardous waste incineration unit that becomes subject to
				  hazardous waste license requirements after October 12, 2005, and no longer
				  apply when an owner or operator of an existing hazardous waste incineration
				  unit demonstrates compliance with the maximum achievable control technology
				  (MACT) requirements of 40 CFR part 63, subpart EEE, by conducting a
				  comprehensive performance test and submitting proof of a postmarked
				  notification of compliance to the department under
				  40 CFR
				  63.1207(j) and
				  63.1210(d)
				  documenting compliance with 40 CFR part 63, subpart EEE. Nevertheless, even
				  after this demonstration of compliance with the MACT standards, hazardous waste
				  license conditions that were based on the standards of this chapter will
				  continue to be in effect until the department removes them from the license or
				  denies, suspends or revokes the license, unless the license expressly provides
				  otherwise.
(b) The MACT standards
				  do not replace the closure requirements of s.
				  NR
				  664.0351 or the applicable requirements of subchs. A
				  to H, BB and CC.
(c) The
				  particulate matter standard of s.
				  NR
				  664.0343(3) remains in effect for
				  incinerators that elect to comply with the alternative to the particulate
				  matter standard of
				  40
				  CFR 63.1206(b) (14) and
				  63.1219(e).
(d) All of the following requirements remain
				  in effect for startup, shutdown and malfunction events if the owner or operator
				  elects to comply with s.
				  NR
				  670.235(1) (a) 1. to minimize
				  emissions of toxic compounds from these events:
1. Section
				  NR
				  664.0345(1) requiring that an
				  incinerator operate according to operating requirements specified in the
				  license.
2. Section
				  NR
				  664.0345(3) requiring compliance with
				  the emission standards and operating requirements during startup and shutdown
				  if hazardous waste is in the combustion chamber, except for particular
				  hazardous wastes.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0341 - Waste analysis

Current through June 24, 2024
(1) As a portion of the trial burn plan
				  required by s.
				  NR
				  670.062, or with the feasibility and plan of operation
				  report, the owner or operator shall have included an analysis of the waste feed
				  sufficient to provide all information required by s.
				  NR
				  670.062(2) or
				  670.019. Owners or operators of new
				  hazardous waste incinerators shall provide the information required by s.
				  NR
				  670.062(3) or
				  670.019 to the greatest extent
				  possible.
(2) Throughout normal
				  operation the owner or operator shall conduct sufficient waste analysis to
				  verify that waste feed to the incinerator is within the physical and chemical
				  composition limits specified in the owner or operator's license (under s.
				  NR
				  664.0345(2) ).
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0342 - Principal organic hazardous constituents (POHCs)

Current through June 24, 2024
(1) The owner or
				  operator shall treat principal organic hazardous constituents (POHCs) in the
				  waste feed to the extent required by the performance standard of s.
				  NR
				  664.0343.
(2)
(a) The
				  department will specify one or more POHCs in the facility's license, from among
				  those constituents in ch. NR 661 Appendix VIII, for each waste feed to be
				  burned. The department will base this specification on the degree of difficulty
				  of incineration of the organic constituents in the waste and on their
				  concentration or mass in the waste feed, considering the results of waste
				  analyses and trial burns or alternative data submitted with the feasibility and
				  plan of operation report. Organic constituents which represent the greatest
				  degree of difficulty of incineration will be those most likely to be designated
				  as POHCs. Constituents are more likely to be designated as POHCs if they are
				  present in large quantities or concentrations in the waste.
(b) The department will designate trial POHCs
				  for performance of trial burns according to the procedure in s.
				  NR
				  670.062 for obtaining trialburn plan
				  approvals.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0343 - Performance standards

Current through June 24, 2024
The owner or operator shall design, construct and maintain
					 an incinerator burning hazardous waste so that, when operated according to
					 operating requirements specified under s.
					 NR
					 664.0345, it will meet all of the following
					 performance standards:
(1)
(a) Except as provided in par. (b), an
				  incinerator burning hazardous waste shall achieve a destruction and removal
				  efficiency (DRE) of 99.99% for each principal organic hazardous constituent
				  (POHC) designated (under s.
				  NR
				  664.0342 ) in its license for each waste feed.
				  Determine the DRE for each POHC using the following equation:
Click to
					 view image
where:
Win = mass feed rate of one
					 principal organic hazardous constituent (POHC) in the waste stream feeding the
					 incinerator
Wout = mass emission rate of the
					 same POHC present in exhaust emissions prior to release to the
					 atmosphere
(b) An
				  incinerator burning hazardous wastes F020, F021, F022, F023, F026 or F027 shall
				  achieve a destruction and removal efficiency (DRE) of 99.9999% for each
				  principal organic hazardous constituent (POHC) designated (under s.
				  NR
				  664.0342 ) in its license. The owner or operator shall
				  demonstrate this performance on POHCs that are more difficult to incinerate
				  than tetra-, penta- and hexachlorodibenzo-p-dioxins and dibenzofurans. The
				  owner or operator shall determine the DRE for each POHC using the equation in
				  par. (a).
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0344 - Hazardous waste incinerator licenses

Current through June 24, 2024
(1) The owner or
				  operator of a hazardous waste incinerator may burn only wastes specified in the
				  owner or operator's license and only under operating conditions specified for
				  those wastes under s.
				  NR
				  664.0345, except in any of the following
				  circumstances:
(a) In approved trial burns
				  under s.
				  NR
				  670.062.
(b) Under exemptions created by s.
				  NR
				  664.0340.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0345 - Operating requirements

Current through June 24, 2024
(1) The owner or
				  operator shall operate an incinerator according to the operating requirements
				  in the license. The department will specify these on a case-by-case basis as
				  those demonstrated (in a trial burn or in alternative data as specified in s.
				  NR
				  664.0344(2) and included with the
				  feasibility and plan of operation report) to be sufficient to comply with the
				  performance standards of s.
				  NR
				  664.0343.
(2) Each set of operating requirements will
				  specify the composition of the waste feed (including acceptable variations in
				  the physical or chemical properties of the waste feed which will not affect
				  compliance with the performance requirement of s.
				  NR 664.0343
				  ) to which the operating requirements apply. For each waste feed to which the
				  operating requirements apply, the license will specify acceptable operating
				  limits including all of the following conditions:
(a) Carbon monoxide (CO) level in the stack
				  exhaust gas.
(b) Waste feed
				  rate.
(c) Combustion
				  temperature.
(d) An appropriate
				  indicator of combustion gas velocity.
(e) Allowable variations in incinerator
				  system design or operating procedures.
(f) Other operating requirements as are
				  necessary to ensure that the performance standards of s.
				  NR 664.0343
				  are met.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0347 - Monitoring and inspections

Current through June 24, 2024
(1) The owner or
				  operator shall conduct, as a minimum, all of the following monitoring while
				  incinerating hazardous waste:
(a) Monitor
				  combustion temperature, waste feed rate and the indicator of combustion gas
				  velocity specified in the facility license on a continuous basis.
(b) Monitor CO on a continuous basis at a
				  point in the incinerator downstream of the combustion zone and prior to release
				  to the atmosphere.
(c) Upon request
				  by the department, sample and analyze the waste and exhaust emissions to verify
				  that the operating requirements established in the license achieve the
				  performance standards of s.
				  NR
				  664.0343.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter O - Incinerators › Section NR 664.0351 - Closure

Current through June 24, 2024
At closure the owner or operator shall remove all hazardous
					 waste and hazardous waste residues (including, but not limited to, ash,
					 scrubber waters and scrubber sludges) from the incinerator
					 site.
At closure, as throughout the operating period, unless
						the owner or operator can demonstrate, according to s. NR 661.0003(4), that the
						residue removed from the incinerator is not hazardous waste, the owner or
						operator becomes a generator of hazardous waste and shall manage it according
						to the applicable requirements of chs.
						NR
						662 to 666.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter S - Special Provisions for Cleanup › Section NR 664.0550 - Applicability of corrective action management unit (CAMU) rules

Current through June 24, 2024
(1) Except as
				  provided in sub. (2), CAMUs are subject to the requirements of s.
				  NR
				  664.0552.
(2) CAMUs that were approved before April 22,
				  2002, or for which substantially complete applications (or equivalents) were
				  submitted to the department on or before November 20, 2000, are subject to the
				  requirements in s.
				  NR
				  664.0551 for grandfathered CAMUs; CAMU waste,
				  activities and design will not be subject to the standards in s.
				  NR
				  664.0552, so long as the waste, activities and design
				  remain within the general scope of the CAMU as approved.
Wisconsin Administrative Code › Department of Natural Resources › NR 600-699 - Environmental Protection - Hazardous Waste Management › Chapter NR 664 - Hazardous Waste Treatment, Storage And Disposal Facility Standards › Subchapter S - Special Provisions for Cleanup › Section NR 664.0551 - Grandfathered corrective action management units (CAMUs)

Current through June 24, 2024
(1) To implement
				  remedies under s.
				  NR
				  664.0101, s. 291.37, Stats., or
				  42 USC
				  6928(h) or to implement
				  remedies at a licensed facility that is not subject to s.
				  NR
				  664.0101, the department may designate an area at the
				  facility as a corrective action management unit under the requirements in this
				  section. In this section, "corrective action management unit" or "CAMU" means
				  an area within a facility that is used only for managing remediation wastes for
				  implementing corrective action or cleanup at the facility. A CAMU shall be
				  located within the contiguous property under the control of the owner or
				  operator where the wastes to be managed in the CAMU originated. One or more
				  CAMUs may be designated at a facility.
(a)
				  Placement of remediation wastes into or within a CAMU does not constitute land
				  disposal of hazardous wastes.
(b)
				  Consolidation or placement of remediation wastes into or within a CAMU does not
				  constitute creation of a unit subject to minimum technology
				  requirements.