(1) GENERAL.
(a) All final cover systems shall be designed
to minimize leachate generation by limiting the amount of percolation through
the cap system, reduce landfill maintenance by stabilizing the final surface
through design of compatible slopes and establishment of vegetation, account
for differential settlement and other stresses on the capping layer, minimize
the climatic effects of freeze-thaw and desiccation on the clay capping layer
of the final cover system, and provide removal of leachate and venting of gas
from those landfills which accept wastes with a high moisture content or which
readily biodegrade.
(b) All new
landfills and expansions of existing landfills shall be designed with a final
cover system meeting the requirements in subs. (2) to (9) unless it is
established to the satisfaction of the department that portions of the final
cover system are not needed based on the proposed waste types and the proposed
design. The geomembrane component in sub. (5) does not apply to landfills
designed exclusively for the disposal of high volume industrial waste, or to
other landfills which are not designed to accept municipal solid waste unless
the landfill is composite lined.
(c) Any phases of an existing landfill which
have been designed and constructed with a composite liner shall be designed and
constructed with a final cover system meeting the requirements in subs. (2) to
(9), except that the requirement for the geomembrane layer in sub. (5) does not
apply to composite lined phases of existing landfills which have completed
final cover placement by July 1, 1996.
(d) Landfills which accept papermill sludges
or other industrial solid wastes with high water contents and low strength may
propose alternate final cover systems if the strength of the waste mass will
not allow for the construction of the cover system required in this
section.
(2) GRADING
LAYER. A minimum 6 inch thick grading layer shall be designed over the final
waste elevation of landfills proposing to accept municipal solid waste to
attain the required slope and provide for a stable base for subsequent system
components. Daily and intermediate cover may be used for this
purpose.
(3) SUPPORT LAYER FOR
LOW-STRENGTH WASTES. A support layer shall be designed for stabilization,
reinforcement and removal of leachate and gas over the final waste elevations
for landfills which accept industrial solid wastes with high water contents and
low strength.
(4) CLAY CAPPING
LAYER. A minimum 2 foot thick clay cap shall be designed to provide a low
hydraulic conductivity barrier to percolation. Clay used for this layer shall
meet the specifications in s.
NR
504.06(2) (a). The clay capping layer
shall be constructed according to s.
NR
504.06(2) (f). Final cover systems
that are required to include a geomembrane layer may be designed with the
following alternatives to the clay component of the composite capping layer:
(a) The clay component of the capping layer
may be replaced by a GCL overlying a minimum of 2 feet of soil barrier layer.
This GCL layer and the soil barrier layer shall meet the following material and
construction specifications:
1. The GCL shall
consist of a layer of sodium bentonite clay encapsulated between 2
geotextiles.
2. The GCL shall be
covered with a geomembrane the same day that it is unpacked and placed in
position. The GCL may not be installed in standing water or during rain. The
GCL shall be dry when installed and covered. A GCL exhibiting unconfined
swelling shall be removed and replaced.
3. The GCL shall be installed in a relaxed
condition and shall be free of tension or stress upon completion of the
installation. The GCL may not be stretched to fit.
4. Adjoining panels of a GCL shall be laid
with a minimum of 6 inches of overlap on the longitudinal seams and a minimum
20 inches of overlap on the panel end seams.
5. Irregular shapes, cuts or tears in the
installed GCL shall be covered with a GCL patch that provides a minimum 12 inch
overlap onto adjacent GCL surfaces.
6. A seal of loose bentonite granules shall
be placed in seam overlaps at a minimum rate of one quarter pound per linear
foot of seam for all panel end seams and longitudinal seams. The seal of loose
bentonite may be deleted, with concurrence by the department, for longitudinal
seams where the manufacturer has processed the overlap area to enhance sealing.
The seal may not be deleted for any longitudinal seams that are transitions
between construction phases.
7.
Loose bentonite or bentonite amended soil shall be placed at all patches and
penetrations.
8. GCL panels shall
be certified needle-free through magnetic and metal detection tests.
9. The GCL shall be placed in direct contact
with a soil barrier layer.
10.
Vehicle traffic on the subgrade of the GCL and on the GCL shall be restricted
to the minimum weight and number of machines needed to deploy the GCL and
geomembrane. Vehicles shall be operated to minimize the formation of ruts and
surface deformations and to prevent damage to the GCL and geomembrane.
Deployment methods shall be selected to prevent any tearing or combing out of
fibers of the GCL.
11. Soil cover
placement over the geosynthetics shall be completed in the same construction
season as the geosynthetic construction.
12. The soil barrier layer shall consist of
fine-grained soil or a well graded sandy soil with fines, meeting the USCS soil
types ML, CL, CH, SM, or SC or dual-symbol classifications of these soils, with
at least 25% by weight passing the P200 sieve size. The upper one foot shall
have a maximum particle size of 2 inches or less. The lower one foot shall have
a maximum particle size of 4 inches or less.
13. The soil barrier layer shall be compacted
in lift heights of no greater than 12 inches after compaction using footed
compaction equipment with feet at least 6 inches long. Each lift shall be
disked or otherwise mechanically processed prior to compaction to break up
clods and allow for moisture content adjustment. Clod size shall be no greater
than 4 inches.
14. A sufficient
number of passes of the compaction equipment shall be made over each lift to
ensure complete remolding of the soil. All compaction equipment utilized shall
have a minimum static weight of 30,000 pounds. Compaction equipment with static
weight that exceeds 15,000 pounds may be utilized where it utilizes vibration
to achieve dynamic compaction that exceeds 30,000 pounds of compaction energy.
Lighter equipment may be used in small areas where it is not possible to use
full size equipment. Alternative procedures or equipment may be proposed for
approval by the department.
15. All
soil shall be compacted to 90% modified or 95% standard Proctor density or
greater at a moisture content at or wet of optimum. As soil placement proceeds,
the minimum density and moisture content targets shall be adjusted as
necessary.
16. Each lift shall be
keyed into clay or soil barrier layer soils in adjacent phases to form a
continuous seal. This shall be accomplished by excavating steps with a minimum
width of 2 feet along the edge of the existing phase and overlapping them with
lifts being placed for the new phase. A minimum of 2 steps shall be
included.
17. The surface of the
top lift shall be graded or compacted to be smooth and firm and shall be
inspected for removal of coarse gravel, cobbles and debris prior to placement
of a GCL.
(b) For
industrial solid waste landfills that predominantly accept compressible wastes
or wastes with high water contents and low strength, the clay layer may be
replaced by a GCL overlying a minimum of a one foot sand layer. The gradation
of the sand layer shall be a uniform sand selected to vent gas, drain leachate
and provide hydration water to the GCL.
(c) For industrial solid waste landfills that
predominantly accept ash, the clay layer may be replaced by a GCL overlying a
minimum of 2 feet of soil barrier layer. The soil barrier layer shall meet the
requirements of par. (a) 13. to 17. The upper foot of soil barrier layer shall
also meet the requirements of par. (a) 12. The lower foot shall be designed to
provide a capillary break between the ash and the upper one foot of soil
barrier layer.
(d) The lower one
foot of the clay layer may be replaced with a minimum of one foot of foundry
green sand system sand with a bentonite content of greater than 6%, a liquid
limit of greater than 20, a plasticity index of greater than 6, and a hydraulic
conductivity of less than 1x10-7 cm/sec. The green sand system sand shall be
compacted to 90% modified or 95% standard Proctor density or greater at a
moisture content at or wet of optimum.
(5) GEOMEMBRANE LAYER. A geomembrane layer
shall be designed to provide a low hydraulic conductivity barrier to
percolation. The design and construction of the geomembrane component of the
final cover system shall meet the requirements of s.
NR
504.06(3) (c) to (j) and the
following:
(a) The nominal geomembrane
thickness shall be 40 mils or greater, with no thickness measurements falling
below industry accepted manufacturing tolerances.
(b) The geomembrane shall be installed in
direct contact with the clay capping layer.
(c) Penetrations of the geomembrane, such as
gas extraction wells, shall be fitted with prefabricated collars of pipe and
membrane or plate and welded at the same angles which the penetrations make
with the final cover slope. Methods of fixing membrane boots to vertical pipes
extending above the geomembrane shall allow for differential settlement of the
waste with respect to the piping without damage to the membrane seal.
(6) DRAINAGE AND ROOTING ZONE
LAYER. A minimum 2.5 foot thick drainage and rooting zone layer shall be
designed above the geomembrane layer or clay capping layer. This layer shall
include a rooting zone to provide additional rooting depth for vegetation and
to protect the geomembrane layer or the clay capping layer from freeze-thaw
damage and other environmental effects. It shall also include a drainage layer
to allow for the drainage of liquid infiltrating through the cap. Soils
available on or near the proposed landfill property may be proposed for the
rooting zone portion of this layer. This layer may not be densely compacted.
(a) For all landfills, a drainage layer shall
be designed immediately above the capping layer. The drainage layer shall
consist of a minimum of one foot of sand with a minimum hydraulic conductivity
of 1x10-3 cm/sec or a geosynthetic drain layer of equivalent or greater flow
capacity. The design shall include an analysis which demonstrates whether the
maximum head in the drain layer will be confined within the thickness of the
drain. Drain calculations shall include infiltration rates based on saturated
characteristics of the topsoil and rooting zone and a hydraulic gradient of one
through the topsoil and rooting zone.
(b) A perimeter drain pipe shall be placed at
the low end of all final cover sideslopes. The drain pipe shall be surrounded
by a minimum of 6 inches of gravel or sand with a minimum hydraulic
conductivity of 1x10-2 cm/sec. The drain pipe shall be sloped to a series of
outlets at spacings no further than every 200 feet. Modeling may be submitted
to the department which supports the proposal of a different spacing.
(7) TOPSOIL. A minimum of 6 inches
of topsoil shall be designed over the cover layer to support the proposed
vegetation. Fertilizer and lime shall be added in accordance with section 630,
Wisconsin department of transportation standard specifications for road and
bridge construction or other appropriate specifications in order to establish a
thick vegetative growth.
(8)
REVEGETATION. The seed type and amount of fertilizer applied shall be proposed
depending on the type and quality of topsoil and compatibility with both native
vegetation and the final use. Unless otherwise approved by the department in
writing, seed mixtures and sowing rates shall be those specified for
right-of-ways according to section 630, 2003 edition of the Wisconsin
department of transportation standard specifications for highway and structure
construction and the 2004 supplemental specifications. Application rates for
fertilizer and mulch shall also be specified.
Note: The 2003 edition of the Wisconsin department of
transportation standard specifications for highway and structure construction
and any annual supplemental specifications are available at
http://www.dot.wisconsin.gov/business/engrserv/procedures.htmor
can be obtained from the department of natural resources, bureau of waste
management, 101 S. Webster Street, P.O. Box 7921, Madison, WI 53707-7921, (608)
266-2111, waste.management@dnr.state.wi.us. Copies are also available for
inspection at the offices of the legislative reference bureau and the secretary
of state.
(9) FINAL USE.
The proposed final use shall be compatible with the final cover system. The
following activities are prohibited at solid waste disposal landfills which are
no longer in operation unless specifically approved by the department in
writing.
(a) Use of the waste disposal area
for agricultural purposes.
(b)
Establishment or construction of any buildings over the waste disposal
area.
(c) Excavation of the final
cover or any waste materials.
Notes
Wis.
Admin. Code Department of Natural
Resources
§
NR
504.07
Cr. Register, January,
1988, No. 385, eff. 2-6-88; am. (1) (a), (b), (2), cr. (1) (c), (d), (5), (6)
(a), (b), r. and recr. (3), (4), r. (5) (a) to (c), renum. (5) to (8) to be (6)
to (9) and am. (6) (intro.), (7), (9) (intro.), (a), (b), Register, June, 1996,
No. 486, eff. 7-1-96; CR 04-077: am. (6) (a) Register November 2005 No. 599,
eff. 12-1-05; CR 05-020: r. and recr. (4), am. (8) Register January 2006 No.
601, eff. 2-1-06.