Utah Admin. Code R315-264-221 - Design and Operating Requirements
(a) Any surface impoundment that is not
covered by Subsection R315-264-221(c) or
40 CFR
265.221, which is adopted by reference, shall
have a liner for all portions of the impoundment, except for existing portions
of such impoundments. The liner shall be designed, constructed, and installed
to prevent any migration of wastes out of the impoundment to the adjacent
subsurface soil or ground water or surface water at any time during the active
life, including the closure period, of the impoundment. The liner may be
constructed of materials that may allow wastes to migrate into the liner, but
not into the adjacent subsurface soil or ground water or surface water, during
the active life of the facility, provided that the impoundment is closed in
accordance with Subsection
R315-264-228(a)(1).
For impoundments that will be closed in accordance with Subsection
R315-264-228(a)(2),
the liner shall be constructed of materials that can prevent wastes from
migrating into the liner during the active life of the facility. The liner
shall be:
(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; and
(3) Installed to cover all surrounding earth
likely to be in contact with the waste or leachate.
(b) The owner or operator shall be exempted
from the requirements of Subsection R315-264-221(a) if the Director finds,
based on a demonstration by the owner or operator, that alternate design and
operating practices, together with location characteristics, shall prevent the
migration of any hazardous constituents, see Subsection
R315-264-93,
into the ground water or surface water at any future time. In deciding whether
to grant an exemption, the Director shall consider:
(1) The nature and quantity of the wastes;
(2) The proposed alternate design
and operation;
(3) The
hydrogeologic setting of the facility, including the attenuative capacity and
thickness of the liners and soils present between the impoundment and ground
water or surface water; and
(4)
All other factors which would influence the quality and mobility of the
leachate produced and the potential for it to migrate to ground water or
surface water.
(c) The
owner or operator of each new surface impoundment unit on which construction
commences after January 29, 1992, each lateral expansion of a surface
impoundment unit on which construction commences after July 29, 1992 and each
replacement of an existing surface impoundment unit that is to commence reuse
after July 29, 1992 shall install two or more liners and a leachate collection
and removal system between such liners. "Construction commences" is as defined
in Section
R315-260-10 under
"existing facility".
(1)
(i) The liner system shall include:
(A) A top liner designed and constructed of
materials, e.g., a geomembrane, to prevent the migration of hazardous
constituents into such liner during the active life and post-closure care
period; and
(B) A composite bottom
liner, consisting of at least two components. The upper component shall be
designed and constructed of materials, e.g., a geomembrane, to prevent the
migration of hazardous constituents into this component during the active life
and post-closure care period. The lower component shall be designed and
constructed of materials to minimize the migration of hazardous constituents if
a breach in the upper component were to occur. The lower component shall be
constructed of at least 3 feet, 91 cm, of compacted soil material with a
hydraulic conductivity of no more than 1×10-7 cm/sec.
(ii) The liners shall comply with
Subsections R315-264-221(a)(1), (2), and (3).
(2) The leachate collection and removal
system between the liners, and immediately above the bottom composite liner in
the case of multiple leachate collection and removal systems, is also a leak
detection system. This leak detection system shall be capable of detecting,
collecting, and removing leaks of hazardous constituents at the earliest
practicable time through all areas of the top liner likely to be exposed to
waste or leachate during the active life and post-closure care period. The
requirements for a leak detection system in Subsection R315-264-221(c)(2) are
satisfied by installation of a system that is, at a minimum:
(i) Constructed with a bottom slope of one
percent or more;
(ii) Constructed
of granular drainage materials with a hydraulic conductivity of 1 x 10-1 cm/sec
or more and a thickness of 12 inches (30.5 cm) or more; or constructed of
synthetic or geonet drainage materials with a transmissivity of 3 x 10-4 m
2/sec or more;
(iii) Constructed of materials that are
chemically resistant to the waste managed in the surface impoundment and the
leachate expected to be generated, and of sufficient strength and thickness to
prevent collapse under the pressures exerted by overlying wastes and any waste
cover materials or equipment used at the surface impoundment;
(iv) Designed and operated to minimize
clogging during the active life and post-closure care period; and
(v) Constructed with sumps and liquid removal
methods, e.g., pumps, of sufficient size to collect and remove liquids from the
sump and prevent liquids from backing up into the drainage layer. Each unit
shall have its own sump(s). The design of each sump and removal system shall
provide a method for measuring and recording the volume of liquids present in
the sump and of liquids removed.
(3) The owner or operator shall collect and
remove pumpable liquids in the sumps to minimize the head on the bottom liner.
(4) The owner or operator of a
leak detection system that is not located completely above the seasonal high
water table shall demonstrate that the operation of the leak detection system
will not be adversely affected by the presence of ground water.
(d) The Director may approve
alternative design or operating practices to those specified in Subsection
R315-264-221(c) if the owner or operator demonstrates to the Director that such
design and operating practices, together with location characteristics:
(1) Will prevent the migration of any
hazardous constituent into the ground water or surface water at least as
effectively as the liners and leachate collection and removal system specified
in Subsection R315-264-221(c); and
(2) Will allow detection of leaks of
hazardous constituents through the top liner at least as effectively.
(e) The double liner
requirement set forth in Subsection R315-264-221(c) may be waived by the
Director for any monofill, if:
(1) The
monofill contains only hazardous wastes from foundry furnace emission controls
or metal casting molding sand, and such wastes do not contain constituents
which would render the wastes hazardous for reasons other than the toxicity
characteristic in Section
R315-261-24;
and
(2)
(i)
(A) The
monofill has at least one liner for which there is no evidence that such liner
is leaking. For the purposes of Subsection R315-264-221(e), the term "liner"
means a liner designed, constructed, installed, and operated to prevent
hazardous waste from passing into the liner at any time during the active life
of the facility, or a liner designed, constructed, installed, and operated to
prevent hazardous waste from migrating beyond the liner to adjacent subsurface
soil, ground water, or surface water at any time during the active life of the
facility. In the case of any surface impoundment which has been exempted from
the requirements of Subsection R315-264-221(c) on the basis of a liner
designed, constructed, installed, and operated to prevent hazardous waste from
passing beyond the liner, at the closure of such impoundment, the owner or
operator shall remove or decontaminate all waste residues, all contaminated
liner material, and contaminated soil to the extent practicable. If all
contaminated soil is not removed or decontaminated, the owner or operator of
such impoundment will comply with appropriate post-closure requirements,
including but not limited to ground-water monitoring and corrective action;
(B) The monofill is located more
than one-quarter mile from an "underground source of drinking water," as that
term is defined in Section
R315-270-2;
and
(C) The monofill is in
compliance with generally applicable ground-water monitoring requirements for
facilities with permits under Section
19-6-108;
or
(ii) The owner or
operator demonstrates that the monofill is located, designed and operated so as
to assure that there will be no migration of any hazardous constituent into
ground water or surface water at any future time.
(f) The owner or operator of any
replacement surface impoundment unit is exempt from Subsection R315-264-221(c)
if:
(1) The existing unit was constructed in
compliance with the design standards of sections 3004 (o)(1)(A)(i) and (o)(5)
of the Resource Conservation and Recovery Act; and
(2) There is no reason to believe that the
liner is not functioning as designed.
(g) A surface impoundment shall be designed,
constructed, maintained, and operated to prevent overtopping resulting from
normal or abnormal operations; overfilling; wind and wave action; rainfall;
run-on; malfunctions of level controllers, alarms, and other equipment; and
human error.
(h) A surface
impoundment shall have dikes that are designed, constructed, and maintained
with sufficient structural integrity to prevent massive failure of the dikes.
In ensuring structural integrity, it shall not be presumed that the liner
system will function without leakage during the active life of the unit.
(i) The Director shall specify in
the permit all design and operating practices that are necessary to ensure that
the requirements of Section R315-264-221 are satisfied.
Notes
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