Utah Admin. Code R315-322-5 - Standards for Design
(1) Surface
impoundments shall be designed, maintained, and operated to meet the following
requirements found in Section R315-322-5.
(2) Surface impoundments shall be designed
for 55 acre-feet of water or less, unless otherwise approved by the
director.
(3) Surface impoundment
levees shall be constructed so that the inside grade of the levee is no steeper
than 3:1 and the outside grade no steeper than 2:1.
(a) The top of the levee shall have a 2%
cross slope toward the surface impoundment and be of sufficient width to allow
for adequate anchoring of liner components and compaction.
(b) Vertical height of the levees may not
exceed 25% of the total vertical depth of the surface impoundment.
(4) Unloading structures.
(a) The owner or operator shall submit
detailed construction and installation diagrams of each unloading structure and
an explanation of methods that control flow and prevent undesired waste from
entering the solid waste surface impoundment, including hydrocarbons.
(b) Unloading structures shall be designed,
maintained, and operated to adequately process the waste received each
day.
(c) Unloading structures shall
be designed with a leak detection system unless determined unnecessary by the
director.
(5) The design,
construction, and operation of any dewatering or other stabilization or
treatment technique used in association with a solid waste surface impoundment
shall comply with the requirements in Subsection
R315-303-3(2)(b).
(6) Solid waste surface impoundments and
associated enhanced evaporation systems shall be designed to prevent surface or
subsurface discharge of water, and detailed information shall be submitted to
demonstrate control features. Enhanced evaporation systems shall be located no
closer than 100 feet from a facility's exterior boundary.
(7) Any container or tank storage area used
to manage waste containing free liquids shall have secondary containment that:
(a) is free of cracks or gaps and is
sufficiently impervious to contain leaks, spills, and accumulated precipitation
until the collected material is detected and removed;
(b) is sloped or otherwise designed and
operated to drain and remove liquids resulting from leaks, spills, or
precipitation;
(c) has sufficient
capacity to contain 10% of the volume of containers or the volume of the
largest container, whichever is greater. Containers that do not contain free
liquids need not be considered in this determination;
(d) is designed and operated to prevent
run-on into the containment system unless the system has sufficient excess
capacity in addition to that required in Subsection R315-322-5(7)(c) to contain
any run-on that might enter the system; and
(e) is operated to remove spilled or leaked
waste and accumulated precipitation from the sump or collection area in as
timely a manner as is necessary to prevent overflow of the collection
system.
(8) The owner or
operator of a solid waste surface impoundment shall design the facility to
control storm water run-on and run-off as specified in Subsections
R315-303-3(1)(c)
and R315-303-3(1)(d).
(9) The owner or operator of a solid waste
surface impoundment shall design the impoundment to meet the applicable
requirements of Subsection
R315-303-3(8),
except that the standards for groundwater protection are found in Subsection
R315-322-5(11).
(a) In addition to the
signage requirements of Subsection
R315-303-3(8)(d),
the owner or operator of Class VII solid waste surface impoundment shall erect
a sign displaying the facility operator.
(b) In addition to the signage requirements
of Subsection R315-303-3(8)(d),
the owner or operator of Class VII solid waste surface impoundment located in
Duchesne County or Uintah County shall erect a sign displaying the facility
operator and the location using the Public Land Survey
System.
(10) The owner or
operator of a solid waste surface impoundment shall provide design drawings and
as built drawings signed and sealed by a professional engineer according to
Subsection R315-303-3(7).
(11) Groundwater Protection.
(a) The owner or operator of a solid waste
surface impoundment shall comply with the groundwater standard for performance
in Subsection R315-303-2(1)
and shall be subject to the corrective action requirements of Section
R317-6-6.15 as applicable.
(b) The
owner or operator of a new solid waste surface impoundment or lateral expansion
of an existing solid waste surface impoundment shall either:
(i) meet the groundwater alternative or
waiver found in Subsection
R315-302-1(2)(e)(vi);
(ii) monitor the groundwater
beneath the impoundment as specified in Rule R315-308; or
(iii) install and maintain leak detection
equipment and conduct monitoring according to Subsection
R315-322-5(13).
(c) The
owner or operator of an existing solid waste surface impoundment may not
receive hazardous waste from a very small quantity generator unless the
requirements of Subsection R315-322-5(11)(a) are met and no groundwater
assessment or corrective action measures are required under Section
R317-6-6.15.
(d) The owner or
operator of an existing solid waste surface impoundment shall maintain existing
groundwater monitoring wells or leak detection equipment and associated
monitoring programs for the life of the facility, unless otherwise determined
by the director.
(e) Groundwater
monitoring wells, leak detection equipment, associated monitoring programs, or
other groundwater monitoring controls may be required for an existing solid
waste surface impoundment as determined by the director.
(12) Synthetic Liners.
(a) Materials used in lining solid waste
surface impoundments shall be impervious and resistant to weather, tears and
punctures, sunlight, and substances that might be contained in the waste
including hydrocarbons, aqueous acids, alkalies, salt, fungi, or other produced
water.
(b) If rigid materials are
used as a liner, leak proof expansion joints shall be provided, or the material
shall be of sufficient thickness and strength to withstand expansion,
contraction, and settling movements in the underlying earth, without
cracking.
(c) Information regarding
the type, thickness, strength, and life span of materials to be used for lining
the surface impoundment and the method of installation shall be included in the
quality control and quality assurance construction plan required by Subsection
R315-310-4(2)(c)(x).
(d) The owner or operator shall submit
procedures to the director for repair of the liner, should leakage occur.
Repair procedures shall be reviewed and signed by a professional engineer and
may include repair procedures prepared by the liner manufacturer. Repair
procedures shall include:
(i) methods used to
remove liquids and solids as necessary from the surface impoundment;
(ii) management of waste removed;
(iii) location of the leak;
(iv) repair of the leak;
(v) testing of the repair; and
(vi) procedures for resuming
operations.
(e) Solid
waste surface impoundments following the groundwater monitoring requirements of
Subsection R315-322-5(11)(b)(ii) shall either meet the liner design
requirements of Subsection
R315-303-3(4),
or the dual liner design standards of Subsection R315-322-5(12)(f).
(f) Solid waste surface impoundments
following the leak detection monitoring requirements of Subsection
R315-322-5(11)(b)(iii) shall be designed with two synthetic liners, an upper
primary and lower secondary liner, with a leak detection system between them.
Synthetic liners shall be installed according to the manufacturer's
instructions.
(i) The upper primary liner
shall be impervious with a hydraulic conductivity no greater than 1 x
10-7 cm/sec and constructed with a minimum 60-mil
HDPE or equivalent liner approved by the director.
(ii) The lower secondary liner shall be
impervious and constructed with a minimum 40-mil HDPE or equivalent liner
approved by the director.
(iii) The
leak detection system between the upper primary and lower secondary liners
shall be constructed with a HDPE geonet or equivalent liner to provide
separation between the upper primary and lower secondary liners and to enable
flow of any leaked fluid through the upper primary liner to the leak detection
observation sump.
(13) Leak Detection System.
(a) The point of compliance shall be the
space between the upper primary and lower secondary liners. The owner or
operator shall submit detailed construction and installation diagrams for the
leak detection system to the director.
(b) The leak detection design shall include a
drainage and collection system placed between the upper primary and lower
secondary liners and sloped to facilitate the earliest possible detection of a
leak.
(c) The leak detection design
shall include a vertical riser outside the dike allowing direct visual
inspection of the sump from the surface. The sump shall be designed:
(i) to be large enough in diameter to allow
for visual observation and sampling of any fluid, and extend to the lowest
elevation of the lower secondary liner of the solid waste surface
impoundment;
(ii) with a removable
top for the sump riser that prevents entry of fluids; and
(iii) with leak detection piping capable of
withstanding destruction resulting from contact with waste, structural loading
from stresses and disturbances from overlying waste and cover materials,
equipment operation, expansion or contraction, and facilitate clean-out
maintenance.
(d) Leak
detection monitoring shall be performed at each riser when liquid waste is
present inside of the impoundment, and shall be:
(i) performed with no greater than five days
between monitoring surveys, and on each day that waste is received in the
impoundment; and
(ii) recorded in
the facility operating record.
(e) Upon detecting a leak, the owner or
operator of a solid waste surface impoundment shall:
(i) provide verbal notification to the
director within 24 hours of detection;
(ii) submit written notification to the
director within five days of detection; and
(iii) submit a written schedule for
conducting repair within 15 days of detection, including the steps required by
the repair plan specified in Subsection R315-322-5(12)(d).
Notes
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