Haw. Code R. § 11-264-314 - Special requirements for bulk and containerized liquids
(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
(2) The
container is very small, such as an ampule; or
(3) The container is designed to hold free
liquids for use other than storage, such as a battery or capacitor;
or
(4) The container is a lab pack
as defined in section 11-264-316 and is disposed of in accordance with section
11-264-316.
(e) Sorbents
used to treat free liquids to be disposed of in landfills must be
nonbiodegradable. Nonbiodegradable sorbents are: materials listed or described
in paragraph (e)(1) of this section; materials that pass one of the tests in
paragraph (e)(2) of this section; or materials that are determined by the EPA
to be nonbiodegradable through the 40 CFR Part 260 petition process.
(1) Nonbiodegradable sorbents.
(i) Inorganic minerals, other inorganic
materials, and elemental carbon (e.g., aluminosilicates, clays, smectites,
Fuller's earth, bentonite, calcium bentonite, montmorillonite, calcined
montmorillonite, kaolinite, micas (illite), vermiculites, zeolites; calcium
carbonate (organic free limestone); oxides/hydroxides, alumina, lime, silica
(sand), diatomaceous earth; perlite (volcanic glass); expanded volcanic rock;
volcanic ash; cement kiln dust; fly ash; rice hull ash; activated
charcoal/activated carbon); or
(ii)
High molecular weight synthetic polymers (e.g., polyethylene, high density
polyethylene (HDPE), polypropylene, polystyrene, polyurethane, polyacrylate,
polynorborene, polyisobutylene, ground synthetic rubber, cross-linked
allylstyrene and tertiary butyl copolymers). This does not include polymers
derived from biological material or polymers specifically designed to be
degradable; or
(iii) Mixtures of
these nonbiodegradable materials.
(2) Tests for nonbiodegradable sorbents.
(i) The sorbent material is determined to be
nonbiodegradable under ASTM Method G21-70 (1984a)-Standard Practice for
Determining Resistance of Synthetic Polymer Materials to Fungi; or
(ii) The sorbent material is determined to be
nonbiodegradable under ASTM Method G22-76 (1984b)-Standard Practice for
Determining Resistance of Plastics to Bacteria; or
(iii) The sorbent material is determined to
be nonbiodegradable under OECD test 301B: [CO2 Evolution
(Modified Sturm Test)].
(f) Effective November 8, 1985, the placement
of any liquid which is not a hazardous waste in a landfill is prohibited unless
the owner or operator of such landfill demonstrates to the director, or the
director determines, that:
(1) The only
reasonably available alternative to the placement in such landfill is placement
in a landfill or unlined surface impoundment, whether or not permitted or
operating under interim status, which contains, or may reasonably be
anticipated to contain, hazardous waste; and
(2) Placement in such owner or operator's
landfill will not present a risk of contamination of any underground source of
drinking water (as that term is defined in
40
CFR 144.3.(1998))
Notes
State regulations are updated quarterly; we currently have two versions available. Below is a comparison between our most recent version and the prior quarterly release. More comparison features will be added as we have more versions to compare.
No prior version found.