reglab/statecodes huggingface dataset:
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-309 - Surveying and recordkeeping

Current through June, 2024
The owner or operator of a landfill must maintain the
					 following items in the operating record required under section
					 11-264-73:
(a) On a map, the exact location and
				  dimensions, including depth, of each cell with respect to permanently surveyed
				  benchmarks; and
(b) The contents of
				  each cell and the approximate location of each hazardous waste type within each
				  cell.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-310 - Closure and post-closure care

Current through June, 2024
(a) At final
				  closure of the landfill or upon closure of any cell, the owner or operator must
				  cover the landfill or cell with a final cover designed and constructed to:
(1) Provide long-term minimization of
				  migration of liquids through the closed landfill;
(2) Function with minimum
				  maintenance;
(3) Promote drainage
				  and minimize erosion or abrasion of the cover;
(4) Accommodate settling and subsidence so
				  that the cover's integrity is maintained; and
(5) Have a permeability less than or equal to
				  the permeability of any bottom liner system or natural subsoils
				  present.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-312 - Special requirements for ignitable or reactive waste

Current through June, 2024
(a)
				  Except as provided in subsection (b), and in section 11-264-316, ignitable or
				  reactive waste must not be placed in a landfill, unless the waste and landfill
				  meet all applicable requirements of chapter 11-268, and:
(1) The resulting waste, mixture, or
				  dissolution of material no longer meets the definition of ignitable or reactive
				  waste under section 11-261-21 or section 11-261-23; and
(2) Subsection 11-264-17(b) is complied
				  with.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-313 - Special requirements for incompatible wastes

Current through June, 2024
Incompatible wastes, or incompatible wastes and materials,
					 (see Appendix V for examples) must not be placed in the same landfill cell,
					 unless subsection
					 11-264-17(b) is
					 complied with.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-314 - Special requirements for bulk and containerized liquids

Current through June, 2024
(a) [Reserved]
(b) 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.
(c) To demonstrate the
				  absence or presence of free liquids in either a containerized or a bulk waste,
				  the following test must be used: Method 9095 (Paint Filter Liquids Test) as
				  described in "Test Methods for Evaluating Solid Waste, Physical/Chemical
				  Methods,'' EPA Publication SW-846, as incorporated by reference in section
				  11-260-11.
(d) Containers holding
				  free liquids must not be placed in a landfill unless:
(1) All free-standing liquid:
(i) has been removed by decanting, or other
				  methods;
(ii) has been mixed with
				  sorbent or solidified so that free-standing liquid is no longer observed; or
(iii) has been otherwise
				  eliminated; or
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-315 - Special requirements for containers

Current through June, 2024
Unless they are very small, such as an ampule, containers
					 must be either:
(a) At least ninety
				  percent full when placed in the landfill; or
(b) Crushed, shredded, or similarly reduced
				  in volume to the maximum practical extent before burial in the
				  landfill.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-316 - Disposal of small containers of hazardous waste in overpacked drums (lab packs)

Current through June, 2024
Small containers of hazardous waste in overpacked drums
					 (lab packs) may be placed in a landfill if the following requirements are
					 met:
(a) Hazardous waste must be
				  packaged in non-leaking inside containers. The inside containers must 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 must be
				  tightly and securely sealed. The inside containers must 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.
(b) The inside containers must 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 subsection 11-264-314(e), to completely
				  sorb all of the liquid contents of the inside containers. The metal outer
				  container must be full after it has been packed with inside containers and
				  sorbent material.
(c) The sorbent
				  material used must not be capable of reacting dangerously with, being
				  decomposed by, or being ignited by the contents of the inside containers, in
				  accordance with subsection 11-264-17(b).
(d) Incompatible wastes, as defined in
				  section 11-260-10, must not be placed in the same outside container.
(e) Reactive wastes, other than cyanide- or
				  sulfide-bearing waste as defined in paragraph 11-261-23(a)(5), must be treated
				  or rendered non-reactive prior to packaging in accordance with subsections (a)
				  through (d). Cyanide-and sulfide-bearing reactive waste may be packed in
				  accordance with subsections (a) through (d) without first being treated or
				  rendered non-reactive.
(f) Such
				  disposal is in compliance with the requirements of chapter 11-268. Persons who
				  incinerate lab packs according to the requirements in paragraph 11-268-42(c)(1)
				  may use fiber drums in place of metal outer containers. Such fiber drums must
				  meet the DOT specifications in
				  49 CFR
				  173.12 and be overpacked according to the
				  requirements in subsection (b).
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter N - LANDFILLS › Section 11-264-317 - Special requirements for hazardous wastes FO20, FO21, FO22, FO23, FO26, and FO27

Current through June, 2024
(a) Hazardous Wastes FO20, FO21, FO22, FO23,
				  FO26, and FO27 must not be placed in any landfill unless the owner or operator
				  operates the landfill in accord with a management plan for these wastes that is
				  approved by the director pursuant to the standards set out in this subsection,
				  and in accord with all other applicable requirements of this chapter. The
				  factors to be considered are:
(1) The volume,
				  physical, and chemical characteristics of the wastes, including their potential
				  to migrate through the soil or to volatilize or escape into the
				  atmosphere;
(2) The attenuative
				  properties of underlying and surrounding soils or other materials;
(3) The mobilizing properties of other
				  materials co-disposed with these wastes; and
(4) The effectiveness of additional
				  treatment, design, or monitoring requirements.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-340 - Applicability

Current through June, 2024
(a) The rules of this subchapter apply to
				  owners and operators of hazardous waste incinerators (as defined in section
				  11-260-10 ), except as section 11-264-1 provides otherwise.
(b) After consideration of the waste analysis
				  included with Part B of the permit application, the director, in establishing
				  the permit conditions, must exempt the applicant from all requirements of this
				  subchapter except section 11-264-341 (Waste analysis) and section 11-264-351
				  (Closure),
(1) If the director finds that the
				  waste to be burned is:
(i) Listed as a
				  hazardous waste in subchapter D of chapter 11-261, solely because it is
				  ignitable (Hazard Code I), corrosive (Hazard Code C) , or both; or
(ii) Listed as a hazardous waste in
				  subchapter D of chapter 11-261, solely because it is reactive (Hazard Code R)
				  for characteristics other than those listed in paragraphs 11-261-23(a) (4) and
				  (5), and will not be burned when other hazardous wastes are present in the
				  combustion zone; or
(iii) A
				  hazardous waste solely because it possesses the characteristic of ignitability,
				  corrosivity, or both, as determined by the test for characteristics of
				  hazardous wastes under subchapter C of chapter 11-261; or
(iv) A hazardous waste solely because it
				  possesses any of the reactivity characteristics described by paragraphs
				  11-261-23(a) (1), (2), (3), (6), (7), and (8), and will not be burned when
				  other hazardous wastes are present in the combustion zone; and
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-341 - Waste analysis

Current through June, 2024
(a) As a portion of
				  the trial burn plan required by section 11-270-62, or with Part B of the permit
				  application, the owner or operator must have included an analysis of the waste
				  feed sufficient to provide all information required by subsection 11-270-62(b)
				  or section 11-270-19. Owners or operators of new hazardous waste incinerators
				  must provide the information required by subsection 11-270-62(c) or section
				  11-270-19 to the greatest extent possible.
(b) Throughout normal operation the owner or
				  operator must conduct sufficient waste analysis to verify that waste feed to
				  the incinerator is within the physical and chemical composition limits
				  specified in his permit (under subsection 11-264-345(b) ).
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-342 - Principal organic hazardous constituent

Current through June, 2024
(a) Principal
				  Organic Hazardous Constituents (POHCs) in the waste feed must be treated to the
				  extent required by the performance standard of section 11-264-343.
(b)
(1) One
				  or more POHCs will be specified in the facility's permit, from among those
				  constituents listed in Appendix VIII of chapter 11-261, for each waste feed to
				  be burned. This specification will be based 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 Part B of the
				  facility's permit application. 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.
(2) Trial POHCs will be designated for
				  performance of trial burns in accordance with the procedure specified in
				  section 11-270-62 for obtaining trial burn permits.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-343 - Performance standards

Current through June, 2024
An incinerator burning hazardous waste must be designed,
					 constructed, and maintained so that, when operated in accordance with operating
					 requirements specified under section
					 11-264-345, it will meet the
					 following performance standards:
(a)
(1) Except as provided in paragraph (a)(2),
				  an incinerator burning hazardous waste must achieve a destruction and removal
				  efficiency (DRE) of 99.99% for each principal organic hazardous constituent
				  (POHC) designated (under section 11-264-342 ) in its permit for each waste
				  feed. DRE is determined for each POHC from the following equation:
Click Here To View
					 Image
where:
Wln=mass feed rate of one principal
					 organic hazardous constituent (POHC) in the waste stream feeding the
					 incinerator
and
Wout=mass emission rate of the same
					 POHC present in exhaust emissions prior to release to the atmosphere.
(2) An incinerator burning
				  hazardous wastes FO20, FO21, FO22, FO23, FO26, or FO27 must achieve a
				  destruction and removal efficiency (DRE) of 99.9999% for each principal organic
				  hazardous constituent (POHC) designated (under section 11-264-342 ) in its
				  permit. This performance must be demonstrated on POHCs that are more difficult
				  to incinerate than tetra-, penta-, and hexachlorodibenzo-p-dioxins and
				  dibenzofurans. DRE is determined for each POHC from the equation in paragraph
				  11-264-343(a)(1). In addition, the owner or operator of the incinerator must
				  notify the director of his intent to incinerate hazardous wastes FO20, FO21,
				  FO22, FO23, FO26, or FO27.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-344 - Hazardous waste incinerator permits

Current through June, 2024
(a) The owner or
				  operator of a hazardous waste incinerator may burn only wastes specified in his
				  permit and only under operating conditions specified for those wastes under
				  section 11-264-345, except:
(1) In approved
				  trial burns under section 11-270-62; or
(2) Under exemptions created by section
				  11-264-340.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-345 - Operating requirements

Current through June, 2024
(a) An incinerator
				  must be operated in accordance with operating requirements specified in the
				  permit. These will be specified on a case-by-case basis as those demonstrated
				  (in a trial burn or in alternative data as specified in subsection
				  11-264-344(b) and included with Part B of a facility's permit application) to
				  be sufficient to comply with the performance standards of section
				  11-264-343.
(b) 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
				  section 11-264-343 ) to which the operating requirements apply. For each such
				  waste feed, the permit will specify acceptable operating limits including the
				  following conditions:
(1) Carbon monoxide
				  (CO) level in the stack exhaust gas;
(2) Waste feed rate;
(3) Combustion temperature;
(4) An appropriate indicator of combustion
				  gas velocity;
(5) Allowable
				  variations in incinerator system design or operating procedures; and
(6) Such other operating requirements as are
				  necessary to ensure that the performance standards of section 11-264-343 are
				  met.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-347 - Monitoring and inspections

Current through June, 2024
(a) The owner or
				  operator must conduct, as a minimum, the following monitoring while
				  incinerating hazardous waste:
(1) Combustion
				  temperature, waste feed rate, and the indicator of combustion gas velocity
				  specified in the facility permit must be monitored on a continuous
				  basis.
(2) CO must be monitored on
				  a continuous basis at a point in the incinerator downstream of the combustion
				  zone and prior to release to the atmosphere.
(3) Upon request by the director, sampling
				  and analysis of the waste and exhaust emissions must be conducted to verify
				  that the operating requirements established in the permit achieve the
				  performance standards of section 11-264-343.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-348 - 11-264-350 - Reserved

Current through June, 2024
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter O - INCINERATORS › Section 11-264-351 - Closure

Current through June, 2024
At closure the owner or operator must remove all hazardous
					 waste and hazardous waste residues (including, but not limited to, ash,
					 scrubber waters, and scrubber sludges) from the incinerator
					 site.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter S - CORRECTIVE ACTION FOR SOLID WASTE MANAGEMENT UNITS › Section 11-264-552 - Corrective Action Management Units (CAMU)

Current through June, 2024
(a) For the purpose
				  of implementing remedies under section 11-264-101 or HRS section
				  342J-36,
				  the director may designate an area at the facility as a corrective action
				  management unit, as defined in section 11-260-10, in accordance with the
				  requirements of this section. One or more CAMUs may be designated at a
				  facility.
(1) Placement of remediation wastes
				  into or within a CAMU does not constitute land disposal of hazardous
				  wastes.
(2) Consolidation or
				  placement of remediation wastes into or within a CAMU does not constitute
				  creation of a unit subject to minimum technology requirements.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter S - CORRECTIVE ACTION FOR SOLID WASTE MANAGEMENT UNITS › Section 11-264-553 - Temporary Units (TU)

Current through June, 2024
(a) For temporary
				  tanks and container storage areas used for treatment or storage of hazardous
				  remediation wastes, during remedial activities required under section
				  11-264-101 or HRS section
				  342J-36,
				  the director may determine that a design, operating, or closure standard
				  applicable to such units may be replaced by alternative requirements which are
				  protective of human health and the environment.
(b) Any temporary unit to which alternative
				  requirements are applied in accordance with subsection (a) shall be:
(1) Located within the facility boundary;
				  and
(2) Used only for treatment or
				  storage of remediation wastes.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter W - DRIP PADS › Section 11-264-570 - Applicability

Current through June, 2024
(a) The requirements of this subchapter apply
				  to owners and operators of facilities that use new or existing drip pads to
				  convey treated wood drippage, precipitation, and/or surface water run-off to an
				  associated collection system. Existing drip pads are those constructed before
				  December 6, 1990 and those for which the owner or operator has a design and has
				  entered into binding financial or other agreements for construction prior to
				  December 6, 1990. All other drip pads are new drip pads. The requirement at
				  paragraph 11-264-573(b)(3) to install a leak collection system applies only to
				  those drip pads that are constructed after December 24, 1992 except for those
				  constructed after December 24, 1992 for which the owner or operator has a
				  design and has entered into binding financial or other agreements for
				  construction prior to December 24, 1992.
(b) The owner or operator of any drip pad
				  that is inside or under a structure that provides protection from precipitation
				  so that neither run-off nor run-on is generated is not subject to regulation
				  under subsection 11-264-573(e) or subsection 11-264-573(f), as
				  appropriate.
(c) The requirements
				  of this subchapter are not applicable to the management of infrequent and
				  incidental drippage in storage yards provided that:
(1) The owner or operator maintains and
				  complies with a written contingency plan that describes how the owner or
				  operator will respond immediately to the discharge of such infrequent and
				  incidental drippage. At a minimum, the contingency plan must describe how the
				  owner or operator will do the following:
(i)
				  Clean up the drippage;
(ii)
				  Document the cleanup of the drippage;
(iii) Retain documents regarding cleanup for
				  three years; and
(iv) Manage the
				  contaminated media in a manner consistent with State regulations.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter W - DRIP PADS › Section 11-264-571 - Assessment of existing drip pad integrity

Current through June, 2024
(a) For each
				  existing drip pad as defined in section 11-264-570, the owner or operator must
				  evaluate the drip pad and determine that it meets all of the requirements of
				  this subchapter, except the requirements for liners and leak detection systems
				  of subsection 11-264-573(b). No later than the effective date of this rule, the
				  owner or operator must obtain and keep on file at the facility a written
				  assessment of the drip pad, reviewed and certified by an independent, qualified
				  registered professional engineer that attests to the results of the evaluation.
				  The assessment must be reviewed, updated and re-certified annually until all
				  upgrades, repairs, or modifications necessary to achieve compliance with all of
				  the standards of section 11-264-573 are complete. The evaluation must document
				  the extent to which the drip pad meets each of the design and operating
				  standards of section 11-264-573, except the standards for liners and leak
				  detection systems, specified in subsection 11-264-573(b).
(b) The owner or operator must develop a
				  written plan for upgrading, repairing, and modifying the drip pad to meet the
				  requirements of subsection 11-264-573(b), and submit the plan to the director
				  no later than two years before the date that all repairs, upgrades, and
				  modifications are complete. This written plan must describe all changes to be
				  made to the drip pad in sufficient detail to document compliance with all the
				  requirements of section 11-264-573. The plan must be reviewed and certified by
				  an independent qualified registered professional engineer.
(c) Upon completion of all upgrades, repairs,
				  and modifications, the owner or operator must submit to the director, the
				  as-built drawings for the drip pad together with a certification by an
				  independent qualified registered professional engineer attesting that the drip
				  pad conforms to the drawings.
(d)
				  If the drip pad is found to be leaking or unfit for use, the owner or operator
				  must comply with the provisions of subsection 11-264-573(m) or close the drip
				  pad in accordance with section 11-264-575.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter W - DRIP PADS › Section 11-264-572 - Design and installation of new drip pads

Current through June, 2024
Owners and operators of new drip pads must ensure that the
					 pads are designed, installed, and operated in accordance with one of the
					 following:
(a) all of the requirements
				  of sections 11-264-573 (except paragraph 11-264-573(a) (4) ) , 11-264-574 and
				  11-264-575, or
(b) all of the
				  requirements of sections 11-264-573 (except subsection 11-264-573(b) ),
				  11-264-574 and 11-264-575.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter W - DRIP PADS › Section 11-264-573 - Design and operating requirements

Current through June, 2024
(a) Drip pads must:
(1) Be constructed of non-earthen materials,
				  excluding wood and non-structurally supported asphalt;
(2) Be sloped to free-drain treated wood
				  drippage, rain and other waters, or solutions of drippage and water or other
				  wastes to the associated collection system;
(3) Have a curb or berm around the
				  perimeter;
(4)
(i) Have a hydraulic conductivity of less
				  than or equal to 1x10-7 centimeters per second,
				  e.g., existing concrete drip pads must be sealed, coated, or covered with a
				  surface material with a hydraulic conductivity of less than or equal to
				  1x10-7 centimeters per second such that the entire
				  surface where drippage occurs or may run across is capable of containing such
				  drippage and mixtures of drippage and precipitation, materials, or other wastes
				  while being routed to an associated collection system. This surface material
				  must be maintained free of cracks and gaps that could adversely affect its
				  hydraulic conductivity, and the material must be chemically compatible with the
				  preservatives that contact the drip pad. The requirements of this provision
				  apply only to existing drip pads and those drip pads for which the owner or
				  operator elects to comply with subsection 11-264-572(b) instead of subsection
				  11-264-572(a).
(ii) The owner or
				  operator must obtain and keep on file at the facility a written assessment of
				  the drip pad, reviewed and certified by an independent, qualified registered
				  professional engineer that attests to the results of the evaluation. The
				  assessment must be reviewed, updated and recertified annually. The evaluation
				  must document the extent to which the drip pad meets the design and operating
				  standards of this section, except for subsection (b).
(5) Be of sufficient structural strength and
				  thickness to prevent failure due to physical contact, climatic conditions, and
				  the stress of daily operations, e.g., variable and moving loads such as vehicle
				  traffic, movement of wood, etc.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter W - DRIP PADS › Section 11-264-574 - Inspections

Current through June, 2024
(a) During construction or installation,
				  liners and cover systems (e.g., membranes, sheets, or coatings) must be
				  inspected for uniformity, damage and imperfections (e.g., holes, cracks, thin
				  spots, or foreign materials). Immediately after construction or installation,
				  liners must be inspected and certified as meeting the requirements of section
				  11-264-573 by an independent qualified, registered professional engineer. This
				  certification must be maintained at the facility as part of the facility
				  operating record. After installation, liners and covers must be inspected to
				  ensure tight seams and joints and the absence of tears, punctures, or
				  blisters.
(b) While a drip pad is
				  in operation, it must be inspected weekly and after storms to detect evidence
				  of any of the following:
(1) Deterioration,
				  malfunctions or improper operation of run-on and run-off control
				  systems;
(2) The presence of
				  leakage in and proper functioning of leak detection system;
(3) Deterioration or cracking of the drip pad
				  surface.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter W - DRIP PADS › Section 11-264-575 - Closure

Current through June, 2024
(a) At closure, the owner or operator must
				  remove or decontaminate all waste residues, contaminated containment system
				  components (pad, liners, etc.), contaminated subsoils, and structures and
				  equipment contaminated with waste and leakage, and manage them as hazardous
				  waste.
(b) 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 subsection (a), the owner or operator finds that
				  not all contaminated subsoils can be practicably removed or decontaminated, he
				  must close the facility and perform post-closure care in accordance with
				  closure and post-closure care requirements that apply to landfills (section
				  11-264-310 ). For permitted units, the requirement to have a permit continues
				  throughout the post-closure period. In addition, for the purpose of closure,
				  post-closure, and financial responsibility, such a drip pad is then considered
				  to be a landfill, and the owner or operator must meet all of the requirements
				  for landfills specified in subchapters G and H of this chapter.
(c)
(1) The
				  owner or operator of an existing drip pad, as defined in section 11-264-570,
				  that does not comply with the liner requirements of paragraph 11-264-573(b)(1)
				  must:
(i) Include in the closure plan for the
				  drip pad under section 11-264-112 both a plan for complying with subsection (a)
				  and a contingent plan for complying with subsection (b) in case not all
				  contaminated subsoils can be practicably removed at closure; and
(ii) Prepare a contingent post-closure plan
				  under section 11-264-118 for complying with subsection (b) in case not all
				  contaminated subsoils can be practicably removed at closure.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter X - MISCELLANEOUS UNITS › Section 11-264-600 - Applicability

Current through June, 2024
The requirements in this subchapter apply to owners and
					 operators of facilities that treat, store, or dispose of hazardous waste in
					 miscellaneous units, except as section
					 11-264-1 provides
					 otherwise.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter X - MISCELLANEOUS UNITS › Section 11-264-601 - Environmental performance standards

Current through June, 2024
A miscellaneous unit must be located, designed,
					 constructed, operated, maintained, and closed in a manner that will ensure
					 protection of human health and the environment. Permits for miscellaneous units
					 are to contain such terms and provisions as necessary to protect human health
					 and the environment, including, but not limited to, as appropriate, design and
					 operating requirements, detection and monitoring requirements, and requirements
					 for responses to releases of hazardous waste or hazardous constituents from the
					 unit. Permit terms and provisions shall include those requirements of
					 subchapters I through O and AA through CC of this chapter, chapter 11-270, and
					 40 C.F.R. 146 that are appropriate for the miscellaneous unit being permitted.
					 Protection of human health and the environment includes, but is not limited
					 to:
(a) Prevention of any releases
				  that may have adverse effects on human health or the environment due to
				  migration of waste constituents in the ground water or subsurface environment,
				  considering:
(1) The volume and physical and
				  chemical characteristics of the waste in the unit, including its potential for
				  migration through soil, liners, or other containing structures;
(2) The hydrological and geologic
				  characteristics of the unit and the surrounding area;
(3) The existing quality of ground water,
				  including other sources of contamination and their cumulative impact on the
				  ground water;
(4) The quantity and
				  direction of ground-water flow;
(5)
				  The proximity to and withdrawal rates of current and potential ground-water
				  users;
(6) The patterns of land use
				  in the region;
(7) The potential
				  for deposition or migration of waste constituents into subsurface physical
				  structures, and into the root zone of food-chain crops and other
				  vegetation;
(8) The potential for
				  health risks caused by human exposure to waste constituents; and
(9) The potential for damage to domestic
				  animals, wildlife, crops, vegetation, and physical structures caused by
				  exposure to waste constituents;
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter X - MISCELLANEOUS UNITS › Section 11-264-602 - Monitoring, analysis, inspection, response, reporting, and corrective action

Current through June, 2024
Monitoring, testing, analytical data, inspections,
					 response, and reporting procedures and frequencies must ensure compliance with
					 sections 11-264-601,
					 11-264-15,
					 11-264-33,
					 11-264-75,
					 11-264-76,
					 11-264-77, and
					 11-264-101 as well as meet any
					 additional requirements needed to protect human health and the environment as
					 specified in the permit.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter X - MISCELLANEOUS UNITS › Section 11-264-603 - Post-closure care

Current through June, 2024
A miscellaneous unit that is a disposal unit must be
					 maintained in a manner that complies with section
					 11-264-601 during the post-closure
					 care period. In addition, if a treatment or storage unit has contaminated soils
					 or ground water that cannot be completely removed or decontaminated during
					 closure, then that unit must also meet the requirements of section
					 11-264-601 during post-closure
					 care. The post-closure plan under section
					 11-264-118 must specify the
					 procedures that will be used to satisfy this requirement.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter AA - AIR EMISSION STANDARDS FOR PROCESS VENTS › Section 11-264-1030 - Applicability

Current through June, 2024
(a) The rules in this subchapter apply to
				  owners and operators of facilities that treat, store, or dispose of hazardous
				  wastes (except as provided in section 11-264-1 ).
(b) Except for subsections 11-264-1034(d) and
				  (e), this subchapter applies to process vents associated with distillation,
				  fractionation, thin-film evaporation, solvent extraction, or air or steam
				  stripping operations that manage hazardous wastes with organic concentrations
				  of at least ten ppmw, if these operations are conducted in one of the
				  following:
(1) A unit that is subject to the
				  permitting requirements of chapter 11-270, or
(2) A unit (including a hazardous waste
				  recycling unit) that is not exempt from permitting under the provisions of
				  section 11-262-34(a) (i.e., a hazardous waste recycling unit that is not a
				  "90-day" tank or container) and that is located at a hazardous waste management
				  facility otherwise subject to the permitting requirements of chapter 11-270,
				  or
(3) A unit that is exempt from
				  permitting under the provisions of section 11-262-34(a) (i.e., a 90-day tank or
				  container) and is not a recycling unit under the provisions of section
				  11-261-6.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter AA - AIR EMISSION STANDARDS FOR PROCESS VENTS › Section 11-264-1032 - Standards: Process vents

Current through June, 2024
(a) The owner or
				  operator of a facility with process vents associated with distillation,
				  fractionation, thin-film evaporation, solvent extraction, or air or steam
				  stripping operations managing hazardous wastes with organic concentrations of
				  at least ten ppmw shall either:
(1) Reduce
				  total organic emissions from all affected process vents at the facility below
				  1.4 kg/h (3 lb/h) and 2.8 Mg/yr (3.1 tons/yr), or
(2) Reduce, by use of a control device, total
				  organic emissions from all affected process vents at the facility by
				  ninety-five weight percent.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter AA - AIR EMISSION STANDARDS FOR PROCESS VENTS › Section 11-264-1034 - Test methods and procedures

Current through June, 2024
(a) Each owner or
				  operator subject to the provisions of this subchapter shall comply with the
				  test methods and procedures requirements provided in this section.
(b) When a closed-vent system is tested for
				  compliance with no detectable emissions, as required in subsection
				  11-264-1033(1), the test shall comply with the following requirements:
(1) Monitoring shall comply with Reference
				  Method 21 in 40 CFR Part 60.
(2)
				  The detection instrument shall meet the performance criteria of Reference
				  Method 21.
(3) The instrument shall
				  be calibrated before use on each day of its use by the procedures specified in
				  Reference Method 21.
(4)
				  Calibration gases shall be:
(i) Zero air
				  (less than ten ppm of hydrocarbon in air).
(ii) A mixture of methane or n-hexane and air
				  at a concentration of approximately, but less than, ten thousand ppm methane or
				  n-hexane.
(5) The
				  background level shall be determined as set forth in Reference Method
				  21.
(6) The instrument probe shall
				  be traversed around all potential leak interfaces as close to the interface as
				  possible as described in Reference Method 21.
(7) The arithmetic difference between the
				  maximum concentration indicated by the instrument and the background level is
				  compared with five-hundred ppm for determining compliance.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter AA - AIR EMISSION STANDARDS FOR PROCESS VENTS › Section 11-264-1035 - Recordkeeping requirements

Current through June, 2024
(a)
(1) Each owner or operator subject to the
				  provisions of this subchapter shall comply with the recordkeeping requirements
				  of this section.
(2) An owner or
				  operator of more than one hazardous waste management unit subject to the
				  provisions of this subchapter may comply with the recordkeeping requirements
				  for these hazardous waste management units in one recordkeeping system if the
				  system identifies each record by each hazardous waste management
				  unit.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter AA - AIR EMISSION STANDARDS FOR PROCESS VENTS › Section 11-264-1036 - Reporting requirements

Current through June, 2024
(a) A semiannual
				  report shall be submitted by owners and operators subject to the requirements
				  of this subchapter to the director by dates specified by the director. The
				  report shall include the following information:
(1) The EPA identification number, name, and
				  address of the facility.
(2) For
				  each month during the semiannual reporting period, dates when the control
				  device exceeded or operated outside of the design specifications as defined in
				  paragraph 11-264-1035(c) (4) and as indicated by the control device monitoring
				  required by subsection 11-264-1033(f) and such exceedances were not corrected
				  within twenty-four hours, or that a flare operated with visible emissions as
				  defined in subsection 11-264-1033(d) and as determined by Method 22 monitoring,
				  the duration and cause of each exceedance or visible emissions, and any
				  corrective measures taken.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter AA - AIR EMISSION STANDARDS FOR PROCESS VENTS › Section 11-264-1037 - 11-264-1049 - Reserved

Current through June, 2024
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter BB - AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS › Section 11-264-1050 - Applicability

Current through June, 2024
(a) The rules in this subchapter apply to
				  owners and operators of facilities that treat, store, or dispose of hazardous
				  wastes (except as provided in section 11-264-1 ).
(b) Except as provided in subsection
				  11-264-1064(k), this subchapter applies to equipment that contains or contacts
				  hazardous wastes with organic concentrations of at least ten percent by weight
				  that are managed in one of the following:
(1)
				  A unit that is subject to the permitting requirements of chapter 11-270,
				  or
(2) A unit (including a
				  hazardous waste recycling unit) that is not exempt from permitting under the
				  provisions of section 11-262-34(a) (i.e., a hazardous waste recycling unit that
				  is not a "90-day" tank or container) and that is located at a hazardous waste
				  management facility otherwise subject to the permitting requirements of chapter
				  11-270, or
(3) A unit that is
				  exempt from permitting under the provisions of section 11-262-34(a) (i.e., a
				  "90-day" tank or container) and is not a recycling unit under the provision of
				  section 11-261-6.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter BB - AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS › Section 11-264-1051 - Definitions

Current through June, 2024
As used in this subchapter, all terms shall have the
					 meaning given them in section
					 11-264-1031, HRS chapter 342J, and
					 chapters 11-260 through 11-266.
Hawaii Administrative Rules › Title 11 - DEPARTMENT OF HEALTH › Subtitle 1 - GENERAL DEPARTMENTAL PROVISIONS › Chapter 264 - HAZADOUS WASTE MANAGEMENT STANDARDS FOR OWNERS AND OPERATERS OF HAZADOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES › Subchapter BB - AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS › Section 11-264-1052 - Standards: Pumps in light liquid service

Current through June, 2024
(a)
(1) Each pump in light liquid service shall
				  be monitored monthly to detect leaks by the methods specified in subsection
				  11-264-1063(b), except as provided in subsections (d), (e), and (f).
(2) Each pump in light liquid service shall
				  be checked by visual inspection each calendar week for indications of liquids
				  dripping from the pump seal.