United States
                    Environmental Protection
                    Agency
Laboratory
                    Research and Development
EPA-600/S2-83-055  Aug. 1983
&EPA          Project Summary
                    Standardized  Procedures  for
                    Planting  Vegetation  on
                    Completed  Sanitary  Landfills

                    Edward F. Oilman, Franklin B. Flower, and Ida A. Leone
                      A manual was developed for those
                    charged with establishing a vegetative
                    cover on completed landfills. Special
                    problems  associated with grownig
                    plants on these sites are discussed, and
                    step-by-step procedures  are given for
                    converting a closed landfill to a variety
                    of end uses requiring  a  vegetative
                    cover.  Instructions  are  given  for
                    vegetating landfills with  either limited
                    or adequate funds. A hypothetical case
                    of landfill conversion is also included.
                      This Project Summary was developed
                    by  EPA's  Municipal Environmental
                    Research Laboratory, Cincinnati, OH,
                    to announce  key  findings of  the
                    research  project that  is  fully
                    documented in a separate report of the
                    same title (see Project Report ordering
                    information at back).

                    Introduction
                      Completed landfills throughout  the
                    United States are being developed into
                    parks, golf courses,  nature  areas, and
                    other multiple-use facilities. An effective
                    vegetative stand must be established and
                    maintained  on  the final  cover soil to
                    achieve one of these successful end uses,
                    however. This manual was  written for
                    those charged with establishing such a
                    vegetative cover.
                      Step-by-step procedures are given for
                    vegetating a  completed  landfill  with
                    either limited or adequate funds.  Each
                    step is to be performed in sequence. A
                    hypothetical case of landfill conversion to
                    a multiple-use recreational facility is also
                    described to illustrate the  procedures
                    outlined in the manual. This hypothetical
                    site includes a nine-hole golf course,
                    botanical garden, toboggan  run,  picnic
area, nature area, tree and shrub nursery,
bicycle paths, and campgrounds.
  Data were collected from more than 60
site visits in 21 states, other field experi-
ences,  textbooks,  and  standard
references on the growth of plants under
adverse conditions.

Vegetating Landfills with
Limited Funds
Step A-1. Selecting an End Use

  An end use should be selected as soon
as possible. In  cases where funds are
limited, the plan might include a park, a
hunting ground, or a natural open space
for trees, shrubs, and grasses. Intensive
recreational uses such as golf courses
require greater expenditures.

Step A-2. Determining Depth of
Cover
  Cover soil must be at least 60 cm deep
for grass establishment and 90 cm for
trees. Soil depth can be determined with
a backhoe or a soil auger and shovel. A
minimum of one hole per acre should be
dug for large sites (50  acres) and two
holes per acre for smaller  areas. When
funds are limited, trees  may be planted
wherever 90 cm of cover soil exists, or
soil maybe moved from one section of the
site to the area desired for tree planting.

Step A-3. Establishing an
Erosion Control Program
  The soil  on recently covered landfills
must be stabilized soon after spreaing to
prevent erosion. Because the  soil  is
frequently of poor quality and growing
conditions  are often adverse, a one-
growing-season  study   should  be

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conducted  to  select  landfill-tolerant
grasses.  Seeds should be  handspread
and raked into the soil. Mulch and tack
should be usedto hold the seed in place in
sloping areas and to conserve moisture.
Microterracing is  recommended before
seeding and mulching for steep, sloping
ground. Grass and ground cover growth
should be evaluated once a month by a
qualified specialist during the first 4 to 6
months.

Step  A-4. Determining the Soil
Nutrient Status
   Before or during the grass and ground
cover experiments, soil tests should be
made for pH, major nutrients (nitrogen,
potassium,  and  phosphorus),
conductivity,  bulk  density, and organic
matter. Samples should be collected over
the entire landfill in a number of areas
within the proposed planting sites.  The
local county  agricultural agent or  soil
conservation  service  office can  help
evaluate  site specific  problems  and
recommend  the addition  of fertilizer or
lime.

Step A-5. Determining Soil Bulk
Density
   Cover  soil is frequently compacted by
landfill  equipment  during spreading
operations to bulk densities that  will
severely restrict plant root growth. Bulk
density can  be determined  by weighing
two or three  undisturbed soil cores of a
known value for each acre. Compacted
soil should  at least  be scarified  and
organic  matter  should  be added to
enhance the physical properties.

Step A-6. Amending Cover Soil
   The soil over the entire planting area
should be amended with lime, fertilizer,
and/or organic matter according to the
recommendations  from  the  soils
laboratory one to several weeks before
planting. These  materials  should  be
incorporated  into the top  15 cm of soil.

Step A-7.  Selecting Landfill-
Tolerant Species
   Grasses and other ground covers can
be selected for planting in the soil cover
by evaluating the results of the experi-
mental  plots established  earlier  to
determine landfill-tolerant species.

Step  A-8. Planting Grass and
Ground Covers

   No studies have been  done to define
the best planting  techniques for estab-
lishing grasses on  landfills,  but  it is
generally desirable to embed the seed in
the soil. Mulches  have been used as an
alternative to embedding  the  seed, but
this approach is less likely to be effective
on adverse growing sites such as landfills.
Mulches  must be  used  on steep slopes
where embedding or drilling is impossible.
Special techniques such as hydroseeding
may be used on steep slopes inaccessible
to  conventional   equipment.  Gently
sloping or flat sites may be planted by any
of a number of methods (hand spreading,
cyclone spreading, drilling,furrowing, etc.).
Barren areas  where plants will not grow
because of high landfill gas concentra-
tions  may have to be landscaped with
wood chips  or large stones to prevent
erosion   and  provide  a   pleasing
appearance.


Step A-9. Developing Tree and
Shrub Growth
  Trees and shrubs should not be planted
for 1  or  2 years  after  grass  has  been
planted. If the grass cannot grow because
of gases  from the landfill, other deeper-
rooted species  are  not likely to thrive
either.
  To  develop a  good cover  of woody
plants, 90 cm of soil must be in place. If
funds are available, a barrier  should be
placed beneath each tree-planting area to
protect the root system  from harmful
landfill gases.


 Vegetating Landfills with
 Adequate  Funds
 Step B-1. Constructing  the
 Landfill
   A  successful  vegetation program  is
 more likely to be  implemented if the end
 use  plan has been established before
 construction  or closure of the landfill.  If
 such a plan  has  been  developed, steps
 can  then  be taken  to  minimize gas
 production   and   surface   settlement
 accordingly. Final contouring can also be
 planned to hinder erosion and promote
 vegetation.


 Step B-2.  Extracting Gas
   The most  successful  landfill-to-park
 conversions  will   incorporate  a  gas
 extraction system in the landfill to reduce
 the volume of gases escaping into the
 final soil cover and inhibiting root growth.
 These systems will be compatible with
 gas  recovery  operations   and   may
 eventually pay for some park construction
 and maintenance.
Step B-3. Selecting Gas Barriers
  Landfill gases may migrate into the
final cover soil even with a commercial
gas extraction system in operation. The
best procedure  is to cover the entire
landfill with an impervious  soil  layer or
synthetic membrane to keep gases from
entering the final cover soil. But if funds
are not  available for such extensive
barriers, they should at least be installed
i n areas where trees and shrubs are to be
planted.
  A  variety  of  barriers  are  currently
available  to  control  gas  migration,
including a 30- to 60-cm-thick  layer of
impermeable clay followed by 60+ cm of
fertile soil, polyvinyl chloride,  hypalon,
and other types of membrane sheeting.

Step B-4.  Selecting Cover Soil
    Though  final  cover soils  may be
costly and difficult to  obtain, they are
essential  to  the  success   of  any
revegetation program. A soil should be
chosen with a texture resembling loam
for areas where trees and shrubs will be
planted, since they require looser, deeper
soil for root development than do grasses
and ground  covers. The soil should be
tested for pH, Mg, Ca, P, K, N03, NH4 ,
conductivity, Cu, Fe, Zn, Mn, particle size
distribution,  bulk density,  and  organic
matter. The soil should be tested before it
is delivered  to the site, since it can be
easily amended before or during spread-
ing.

Step B-5. Spreading Cover Soil
  The clay soil layers should be spread
over the final refuse layers to  prevent
infiltration of precipitation.  Final cover
soil should then be placed using special
methods  to  avoid  compacting.  The
avoidance   or   elimination  of these
compacted layers  can  be  the key  to a
successful reclamation project.

Step B-6. Providing Proper Soil
Depth
  Areas in which trees and shrubs are to
be planted should be spread with 90 cm of
cover soil, with the top 20 cm consisting
 of topsoil to accommodate most of the
 fine feeder roots. At least 60 cm of cover
 soil  should  be  spread in  areas where
 grasses and other stabilizing vegetation
 will be grown.

 Step B-7. Locating Areas
 Unsuited for Tree and Shrub
 Growth
  Areas unsuited for tree and shrub
growth  may  be  identified by  several

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indicators:  dead  vegetation,  no
vegetation,  anaerobic  soil,  high  soil
temperatures, and thin cover soil.

Step B-8. Selecting  Tree and
Shrub Material
  Factors to be considered in choosing
tree species to be planted include end use
of the landfill, geographic location, type of
refuse in the landfill, and characteristics
of the species (growth rate, final size,
rooting  depth,  flood   tolerance,
mycorrhizal fungi, and pathology).

Step B-9. Planting and
Maintaining Vegetation
  Special planting  instructions must be
followed for specific areas, species, and
types of planting materials. The principles
of  maintaining  plant  material  on
completed landfills arethe same asthose
for  nonlandfill areas, except that  addi-
tional irrigation is required.

  The  full  report   was  submitted  in
fulfillment of Grant No. CR-807673 by
Rutgers University under the sponsorship
of  the  U.S.  Environmental Protection
Agency.
Edward F. Oilman, Franklin B. Flower, and Ida A. Leone are with Cook College,
  Rutgers University, New Brunswick, NJ 08903.
Robert E. Landreth is the EPA Project Officer (see below).
The complete report, entitled "Standardized Procedures for Planting Vegetation
  on Completed Sanitary Landfills," (Order No. PB 83-241 018; Cost: $8.50,
  subject to change) will be available only from:
       National Technical Information Service
       5285 Port Royal Road
       Springfield.  VA 22161
        Telephone: 703-487-4650
The EPA Project Officer can be contacted at:
       Municipal Environmental Research Laboratory
        U.S. Environmental Protection Agency
        Cincinnati, OH 45268
                                            tfUS GOVERNMENT PRINTING OFFICE 1983-659-W7/7167

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United States
Environmental Protection
Agency
Center for Environmental Research
Information
Cincinnati OH 45268
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