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Guide to Revegetation and Environmental Restoration of Closed
LandfillsA Guide to the Revegetation and Environmental Restoration
of Closed Landfills
October 1999
S T A T E O F C A L I F O R N I A
Gray Davis Governor
•
Linda Moulton-Patterson Board Member
For additional copies of this publication, contact the Integrated
Waste Management Board
Publications Clearinghouse 8800 Cal Center Drive, MS 12
Sacramento, CA 95826 www.ciwmb.ca.gov/Publications/
Publication #213-99-010 Printed on Recycled Paper
Copyright 1999 by the Integrated Waste Management Board. All rights
reserved. This publication, or parts thereof, may not be reproduced
in any form without permission.
This report was prepared by staff of the Integrated Waste
Management Board to provide information or technical assistance.
The statements and conclusions of this report are those of the
Board staff and not
necessarily those of the Board members or the State of California.
The State makes no warranty, expressed or implied, and assumes no
liability for the information contained in the succeeding text.
Any
mention of commercial products or processes shall not be construed
as an endorsement of such products or processes.
The Integrated Waste Management Board (IWMB) does not discriminate
on the basis of disability in access to its programs. IWMB
publications are available in accessible formats upon request by
calling the Public Affairs Office at (916) 255-2296. Persons with
hearing impairments can reach the IWMB through the California Relay
Service,
Preface This guide provides landfill managers, owners, operators,
and local enforcement agencies with information on revegetation and
environmental restoration in the closure of landfills. These
techniques also should prove useful to conservationists in
restoration or other habitat reclamation.
The guide is intended to serve as a bridging document between two
State publications. These publications are Guide to Vegetative
Covers for California Landfills, published by the California
Integrated Waste Management Board (IWMB); and WUCOLS, Water Use
Classification of Landscape Species, prepared by the California
Department of Water Resources. These three documents should provide
the project coordinator with the essentials for revegetation or
environmental restoration. This guide also provides listings of
other references and restoration resources in California.
The guide distinguishes between revegetation and environmental
restoration as follows:
Revegetation involves the placement of plants, horticultural or
native, on a project site. Relatively few, if any, other
environmental restoration techniques will be applied. The plants
can be an arbitrary choice of the project coordinator, with no
regard for native species, their distribution or plant community
design. A landfill configured to engineering specifications and
planted with non-native grasses in regulatory compliance
illustrates simple revegetation. Consideration for county approval
of species should be made.
Environmental restoration will invariably involve revegetation.
But, it also involves the extensive design and naturalization of
project site contours, soil content and vegetative communities. The
intent of environmental restoration is to create a seamless
“repair” by emulating and supporting the native floral and faunal
communities adjacent to and on the project site. The ultimate aim
is for the project to be “assimilated” back into the surrounding
environment.
Environmental restoration is characterized by these elements:
• A detailed reconstruction of the project site topography
(elevations). • Site geomorphology (surface features). • Soil types
conducive to the native plants of the project area. • Surface
hydrology (water features). • Native plant species, their
diversity, and distribution.
Acknowledgement I thank my colleagues who volunteered their time
and effort to review this guide. I especially give thanks to those
who encouraged me to press on, to make this resource available to
them.—Jacques Graber, Author, Associate Engineering Geologist,
Permitting and Enforcement Division, California Integrated Waste
Management Board.
i
Acknowledgement i
Chapter 2. Regulatory Background 3 Regulatory Requirements for
Vegetative Final Cover 4
Elements of Restoration 7Chapter 3. Definition of Vegetative Cover
Layer 7 Role or Purpose of the Vegetative Cover 7 The Degrees of
Vegetative Restoration 7 The Goals of Vegetative Cover Programs
9
Chapter 4. Types of Vegetative Communities 13 The Vegetative Zones
13
Chapter 5. Precipitation and Moisture 17
Chapter 6. Aspects of California’s Vegetation 21 Plant Assemblage
Profiles 21 Plant Communities 22 Compatible Plant Associations
26
Chapter 7. Landfill Vegetative Design 31 Landfill Design
Considerations 31 Additional Uses for Vegetative Cover 38
Chapter 8. Considerations in Vegetation Selection 41 Site-Specific
Considerations 41 Planting Considerations 43 Vegetation Types and
Considerations in Program Planning 45
Chapter 9. Planting of Vegetation 51 Seeding 51 Planting Small
Seedlings, Cuttings or Saplings. 52 Transplantation 52 Sources for
Vegetation 54
Chapter 10. Six Concepts for a Successful Restoration 55
Chapter 11. Maintenance of Vegetation 58 Irrigation 58 Water
Supplies 59 Fertilizing and Plant Nutrition 62 Maintaining Plant
Health 62
ii
Chapter 12. Some Problematic Conditions 69 Irrigation Source Water
Problems 69 False Readings in Soil Water Samples 71 Drainage and
Surface Settling 71 Soil Methane Gas Concentrations 72 Additional
Considerations 74
Chapter 13. Conclusion 79
iii
Chapter 1: Introduction The management and final closure of solid
waste landfills in American society is a relatively new applied
science. In 1795, Georgetown, Virginia, enacted the first ordinance
for waste management in the nation. The ordinance prohibited the
extended storage of refuse on private property or the dumping of it
on a public thoroughfare. In 1873, Los Angeles (population 6,000)
established a garbage and dead animal plot with burial of these
wastes to be three feet below ground level.1
In the 1800s, waste disposal sites were selected based on
convenience, especially in the major metropolitan areas. Sites were
not selected to avoid negative environmental impacts. In San
Francisco (population 149,000), two good examples of unsound
disposal practices could be found. One site was at a once existing
bay at the foot of present day Market Street, and a second site was
located at the north area Marina district. Ships were scuttled in
place and wastes brought in to create the newly reclaimed
waterfronts. This process continued until the desired fill area was
constructed. Because no containment barriers for the waste products
were installed, debris freely scattered into the bay. Planned
compaction of the wastes was not practiced at these sites. This
activity led to calamitous differential settling and damage to or
destruction of streets and building foundations during the Great
Earthquake and Fire of 1906. Evidence of this disposal activity is
discovered with each new construction excavation that occurs in the
Financial District of San Francisco.
Smaller rural communities inland generally located their waste
disposal sites with an “out-of-sight, out-of-mind” philosophy.
Often, these disposal sites would be located where wastes literally
could be shoved over the edge of a canyon or ravine, lost from view
and future concern. Eventually, this strategy would be outgrown as
communities grew larger and the over-the-side technique to dispose
of wastes became less manageable. Burning of wastes, especially at
area fills, took on a more important role as a way to "reduce" the
volume of waste remaining at a community disposal site.
As more municipalities applied this practice with its cumulative
air impacts, and other generators of air pollutants became more
prevalent, a new strategy in waste management had to be devised.
Prompted by the development and implementation of the Clean Air Act
of 1977, and the creation of local Air Pollution Control Districts,
the practice of open burn dumps was brought to a close.
The Integrated Waste Management Act (1989) brought waste management
in California to a higher technical level. The end of open burning,
the closure of these sites, and the opening of new landfills
created new demands on management policy. Managed and planned
closure procedures had to be developed to assure consistent closure
of landfills to protect the public health, safety, and the
environment.
By the 1970s, the general public attained a heightened awareness of
the environment, which led to a more critical perspective on the
closure of disposal sites and their final appearance. The casual
viewer sought a more harmonious result, visually and ecologically,
from the closed landfill.
1 Dr. Aston, R. Lee, “A Brief History of the Disposal of Wastes by
Earth Burial,” AEG News, Winter 1998.
Page 1
As a result, the concepts of revegetation and, finally,
environmental restoration, including “bio-engineering,” are
becoming an accepted part of final closure. Even the use of
vegetation as a moisture-regulating mechanism for the final cover
is gaining some serious consideration.
Today's landfills are found in a spectrum of sizes (1 to 700 acres)
as the old ones close and newer, larger ones open. They are often
located in more environmentally critical areas, either in sensitive
habitat or near urban residential housing. Each facility, when it
closes, results in a long-term visual and environmental impact on
the neighboring community or region.
By current regulation, a newly closed landfill is monitored for
various conditions (leachates, landfill gas, slope stability, etc.)
for a period of 30 years, possibly longer, following its final date
of closure per Title 27, California Code of Regulations (27, CCR),
Section (§) 21180. These sites will remain as permanent monuments
to our waste management practices unless restoration is
achieved.
Environmental restoration is used in the mitigation and restoration
of lands damaged by open pit or strip mining operations and other
development projects involving sensitive lands. These techniques
are coming into their own in landfill closure practices. Research
into revegetation with native plants, and the concepts and
practices of environmental restoration, as practiced in these other
venues, are becoming important in the closure of landfills.
When a landfill closes, the primary intent of its design is to
contain the waste and control the by-products resulting from its
containment. These can include landfill gas, leachates, and the
wastes themselves. The design insures the integrity of the external
cover from settling, wind and water erosion, slope failure, and
seismic damage. The design protects the public from exposure to the
confined wastes.
If a planned postclosure land use is implemented, the landfill site
can be designed to accept the appropriate land use. If no planned
postclosure land use is intended (non- irrigated open space) or the
postclosure project entails a parkland, preserve, or golf course,
the final role of the cover layers is to provide a veneer to
prevent erosion, support a viable plant community, and the chosen
postclosure use facility.
Landfills located in arid and desert regions would impose different
demands on the cover. These landfill covers are expected to support
more sparse vegetative communities or, as an alternative, to be
covered with rock cladding. Cladding helps protect the landfill
from slope failures, or erosion, and in turn, can provide a limited
aesthetic visual buffer. Even desert environmental restoration
practices are being utilized with encouraging results.
With special soil surface treatment, using imprinters and
appropriate plant types, a revegetation program in an arid or
desert environment can provide a secondary use for the public in
the surrounding region. Such a program could provide a desert
wildlife area, and educational park for local schools and other
visitors.
This guide is intended to provide practical information and methods
in the concepts of revegetation and environmental restoration as
applied to solid waste landfills.
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Chapter 2: Regulatory Background To assure some degree of
consistency in the development of final vegetative cover in
landfill closure design, regulatory standards were developed by
both federal and State agencies. These standards primarily apply to
the thickness of the vegetative cover soil layer and its
performance, and the vegetation planting and maintenance protocols.
These regulations are concerned with the use of the vegetative
layer as a protective element in the long-term integrity of the
landfill cover rather than as part of a holistic, integrated,
visual, and environmental reconstruction.
The use of vegetation as a soil and slope-stabilizing component for
final cover can be a reasonably economical and durable slope
protection method. Current research reveals that vegetation can
serve as an effective soil layer binder and moisture transpiration
control system. Vegetation can extract excess moisture from the
cover layer, reducing the potential for saturation and possible
slope failure, especially at the soils interface between the
moisture barrier and the erosion or vegetative layer. Employing a
planned plant community and a successional plant population
introduction technique may ensure successful establishment of the
higher plant types, creating a naturalized vegetation
community.
Developing a more complex landscaped, or ecosystem-based, plant
community that is integrated into the surrounding natural
vegetation ecosystem will require more advanced planning, research,
and effort on the part of the operator. Ultimately, the result can
be economically advantageous and aesthetically rewarding through
reduced maintenance costs, improved plant survival, and possible
wildlife habitat enhancement.
There is no current regulatory requirement that states that native
plants must be used in final vegetative cover, or that the landfill
slope profiling and vegetative cover must reflect the natural
conditions in which the landfill is located. But, through practical
application of more natural slope design and vegetative cover in
mine reclamation projects, the natural and native configurations of
plant communities can be more economical in the long run. Soil
conditions and moisture may not support the non-native plants that
are introduced. Natural pests attack and destroy non-native plants
lacking natural defenses against these pests, or the costs and
efforts of maintaining the non-native vegetation, through
irrigation and pest control, are greater than they would be in
using the native counterparts.
This practice should be applicable to landfills. In addition, the
costs of configuring side- slopes and decks to more natural
profiles should not introduce significant costs, if these details
are designed in the early development of the landfill
closure.
As the public's environmental awareness matures, and urbanization
expands around existing closed landfills, or existing urban
landfills close, placing greater demands on final closure
appearances, the role of environmental restoration as an integrated
part of final cover and vegetation design can assume greater
significance. Additionally, new and larger landfills are being
proposed in remote regions of greater environmental sensitivity.
These restored areas could recover lost habitat or, increase
available rare or endangered species habitat. This effort would not
only improve the chances of survival of native or endangered
species, but it could also enhance the public image of the agencies
or operators that adopt this type of restoration program at these
landfills. A
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project at Coyote Canyon, Orange County, is applying such a program
for the California Gnatcatcher, (Polioptilia californica).
Regulatory Requirements for Vegetative Final Cover The primary
regulatory sources for State and federal standards for closures are
Title 27, California Code of Regulations (27 CCR), and 40 Code of
Federal Regulations (40 CFR), Part 258 (Subtitle D).
State
Title 27, CCR Requirements (formerly 14, CCR and 23, CCR)
Subchapter 5, Article 1, Section (§) 20950(e). For landfills and
for waste piles and surface impoundments that are closed as
landfills, all vegetation for the closed unit’s vegetative cover
shall meet the requirements of Section 21090(a)(3)(A)1, in cases
where the unit does not utilize the mechanically resistant erosion
layer per § 21090(a)(3)(A)2.
Section 21090 (a)(3)(A)1. Closed landfills shall be provided with
an uppermost cover layer consisting of either:
1. Erosion resistance via a vegetative layer. This layer consists
of not less than one foot of soil which:
a. Contains no waste (including leachate). b. Is placed on top of
all portions of the low hydraulic conductivity
layer described in § (a)(2). c. Is capable of sustaining native or
other suitable plant growth. d. Is initially planted and is later
replanted as needed to provide
effective erosion resistance with native or other suitable
vegetation having a rooting depth not exceeding the depth to the
top of the low hydraulic conductivity layer described in § (a)(2).
For any proposed vegetative cover, the discharger shall propose a
species mix which harmonizes with the proposed postclosure land use
and which requires little long term maintenance as feasible by
virtue of its tolerance to the vegetative layer’s soil
conditions.
2. Mechanically erosion-resistant layer. An erosion and ultra
violet light-resistant layer which, by virtue of its composition
and finished-and-maintained grade, resists foreseeable erosion
effects by wind-scour, raindrop impact, and runoff (e.g., a
one-foot-thick layer of cobbles, the interstices of which are
filled with gravel).
California Coastal Commission Should a closure project be located
within the jurisdiction of the California Coastal Commission, the
regulatory standards and requirements of that agency may have to be
addressed (PRC 13053.5(a)).
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Department of Fish and Game Should a closure project be located
within the jurisdiction of the California Department of Fish and
Game, the regulatory standards and requirements of that agency may
have to be addressed (PRC 13053.5(a)).
California Environmental Quality Act (CEQA) All projects in
California must be reviewed in accordance with the California
Environmental Quality Act (CEQA) to determine whether the project
may have a significant impact on the environment. If the project
might have a potential significant impact, mitigation measures may
have to be incorporated into the project to avoid the impact.
Federal
Final Cover Design––40 CFR § 258.60, Subpart F 6.2.1 (a)(3).
Minimize erosion of the final cover by the use of an erosion layer
that contains a minimum 6 inches (60 cm) of earthen material
capable of sustaining native plant growth.
6.2.3. Design criteria for a final cover system should be selected
to ... improve aesthetics.
There are alternatives to the Subtitle D prescriptive standard
cover designs which regulatory agencies can consider and approve
(40 CFR §258.60(b)). The alternatives include:
1. An infiltration layer that achieves an equivalent reduction in
the infiltration as specified in paragraph (a)(2) above.
2. An erosion layer that provides equivalent protection from the
wind and water erosion as specified in paragraph (a)(3)
above.
These alternatives provide an additional design choice that can
broaden the vegetative design options available to an operator
closing a landfill.
U.S. Army Corps of Engineers Because many existing landfills and
sites for potential landfills are located near natural waterways or
may be sites upon which are located sensitive wetlands or vernal
pools, the Army Corps of Engineers may have jurisdictional
involvement under section 404 of the Clean Water Act. This
jurisdictional authority may require a closure project obtain a
permit from the Corps, prior to initiating the project. Dispute
over Corps permit jurisdiction is requiring more scrutiny of
project content and project location.
Page 5
Chapter 3: Elements of Restoration Definition of Vegetative Cover
Layer
Although there is no specific definition identified in the CCR, for
the purposes of State regulation, the vegetative cover layer can be
defined on the basis of compliance with all of the requirements of
27, CCR.
Role or Purpose of the Vegetative Cover When a landfill is closed,
the final design of the structure must incorporate various elements
to serve several functions. The cover layers form the containment
and moisture barriers directly overlying the waste mass, providing
the containment and barrier functions above the waste. This
protects the contents from invasive moisture and protects the
public from exposure. The final layer covering all these preceding
elements is the erosion, or vegetative soil layer. This layer, with
vegetation, helps to prevent erosion, supports the vegetation, and
provides some additional moisture protection.
The operations and containment layers below the waste and the final
cover foundation layer and moisture barrier layer above the waste
are intended to serve as barriers to moisture and gas migration
into or out of the landfill. The final vegetative layer’s intended
purpose, in addition to preventing erosion and enhancing moisture
protection, is to serve as a stable substrate for a
surface-stabilizing plant community on the final cover. The minimum
standard vegetative soil layer thickness in California’s Title 27
requirements is 12-inch minimum thickness. This layer can be
thicker but it may not be any thinner than the minimum. This
minimum standard supersedes the 6-inch federal standard for
Subtitle D for landfills in California.
The vegetation that is planted on the final cover is intended to
serve as a protective soil binding and stabilizing element. The
vegetation can also serve as an attenuator; the canopy absorbing
damaging rainfall velocity before it strikes the soil.
This function of the vegetation aids in reduced impact erosion on
the soil layer and improved moisture capture. Vegetation also
serves as a moisture control through evapotranspiration by removing
excess moisture from the soil, an aesthetic mitigation and an
ecological mitigation by providing a reconstructed vegetative
habitat for local animal species as well as rare or endangered
plant or animal species.
The Degrees of Vegetative Restoration When a landfill is finally
closed and the operator is preparing the final vegetation layer and
the vegetative cover, there are three options to consider:
restoration, aesthetics, and function.
Environmental Restoration Environmental restoration is recreating,
as completely as is practicable, that portion of the ecosystem that
was displaced or disturbed by the project. Restoration takes into
consideration the reconstruction or close approximation of the soil
types and profile or topography of the area that was
Page 7
modified. The reconstructed slopes and terrain will mimic, as
closely as possible, the natural features of the surrounding land.
If the landfill were placed in a canyon, the slopes would be
designed to mimic a shallower canyon or broad slope; or a ridge, if
fill material overfilled the original canyon terrain. Surface
landfills in flatter terrain would be profiled to emulate hill
slopes, if hills are nearby, or to emulate a hill though none are
in the area. Vegetation in such a restoration project would ideally
reflect the proportions of plant species distribution reflected in
the surrounding plant communities, utilizing the same species of
native plants in the revegetation phase.
This type of restoration would serve three important functions. It
would “repair” the ecosystem by replacing the project with the
original environmental composition displaced while the project was
operating. It would provide a new natural environment to enhance
the local biotic community, improving species diversity and
expanding available habitat. Restoration could also provide
mitigative capacity in certain circumstances for mitigation of
endangered species by allowing custom fitting of special localized
habitats for endangered species in an area into the surrounding
natural community. By using native plant species, the restoration
project serves in contributing to the local species gene pool by
providing more indigenous individuals to reproduce with the
established local resident species.
Aesthetic Mitigation—Providing Compatible Postclosure Use Options
If environmental restoration is not a viable option for the
operator, or a proposed postclosure land use development is
intended for the former project site, an aesthetically satisfying
vegetation program can be implemented on the site that approximates
the local vegetation community. Such a vegetation option would be
available for recreational parks or golf courses, or business park
campuses. In this application, horticultural or nursery plant types
and aesthetically designed landscaping are planned, not necessarily
to emulate the natural vegetation and local terrain. Native plants
could also be utilized but with the landscaped accent required for
the project plan. Generally, this type of project will serve two
purposes:
• Space Use The postclosure project will provide a viable natural
environment for the public’s enjoyment. It can provide an
aesthetically pleasing landscape that will mediate visual impacts
created by the closed landfill. The project can still satisfy
native plant needs while exhibiting landscaped features.
• Mitigative Needs The project will provide an acceptable
alternative that will satisfy the regulatory standards of 27, CCR
and Subtitle D. It will also offset the past impacts of the
previous landfill activities.
Regulatory Compliance—Satisfying Regulatory Standards A vegetative
program that is designed to satisfy the requirements of Title 27,
CCR and Subtitle D will employ the simplest and most basic elements
of final cover design, landfill slope profiling, and vegetation
types. Slope profiles will assume the most basic engineered forms
in compliance with the closure requirements. Overall cover
structure surfaces will generally be planar and
Page 8
obviously man-made. The primary functions of the vegetative cover
will be to provide slope stability and soil binding, provide
moisture control, control surface runoff flows, enhance
evapotranspiration, reduce moisture intrusion and leachate
production, and reduce landfill gas production. Vegetation will
assume the more direct functional roles while providing the basic
coverage to satisfy the requirements of Title 27.
In this application, landfill control systems will be least
visually hidden. Gas control systems, vents, well heads, collection
pipes, surface moisture control systems, and maintenance/access
roads will be most visible. A general grass vegetative cover will
be in place. Still, native grasses can be employed in this
situation.
The Goals of Vegetative Cover Programs The goals of vegetative
cover programs may be based upon or dictated by the financial
resources and priorities established by each operator, while
complying with the regulatory requirements of CCR Title 27 and 40
CFR, Subtitle D.
Restorative
The technically most complex project is the restorative vegetation
plan. To properly implement restoration, the operator must
construct (reconstruct) a final cover (erosion or vegetative layer)
that provides soil conditions and topographic features closely
duplicating the surrounding soil types and geography. These
preparations are intended to increase the chances that the
replacement native plant community that is reintroduced will
survive. A restored vegetative plant assemblage must duplicate the
native plant profile in terms of ratios of species occurrence
(distribution), correct native species selected and distribution of
these species across the project site to closely duplicate the
plant distributions in the surrounding undamaged areas. Ideally,
this restoration will create conditions that will provide a natural
habitat to encourage re-population by native animal species. In
theory when this project has matured, it should provide a seamless
restoration with the surrounding land or create a natural native
environment in mixed urban or suburban areas.
An alternative project may involve creation of special habitat for
rare or endangered species that both mitigates the project and
provides new habitat. Conditions may warrant preparation of the
site with special vegetation types that are present in that area
that are attractants of local rare or endangered species,
especially insects, such as certain species of butterfly or beetle,
small reptiles, or mammals.
Characteristics of a Restored Site Restored sites use native
vegetation indigenous to the immediate area, or, for rare and
endangered species mitigation, rare plant species that would be
found within the ecological region. They provide vegetation or
unique habitat that is depended upon by specific species of animals
or insects for food or reproductive needs or as a mitigative effort
to increase populations of a rare or endangered plant.
Page 9
• They provide for a natural plant community profile, with
representative species distributions and correct profile of
understory plants, intermediate shrubs and overstory trees.
• The reconstructed land surface closely mimics the surrounding
natural land features. This is accomplished by using HDPE geogrid
reinforcement, landform contour grading and importing large rocks
or cobbles and placing them on-site, These practices can be
effected if the surrounding terrain demonstrates these features and
if they can be engineered into the final cover design without
compromising final cover functions.
• Restored sites use bioengineering techniques for erosion repair
and slope stabilization efforts including straw logs, wattles,
revetments, and other surface stabilizing structures that can
employ living plant materials in the structures, aiding in slope
profiling and stabilizing.
• The primary projects employing habitat restoration or mitigation
are wildlife preserves, natural parklands, wildlife management
areas, rare or endangered species mitigation, or natural public or
educational parklands.
• Restored sites do not have planned postclosure land uses beyond
the role of parkland or preserve.
In terms of the restorative role of a site, a vegetation plan
designed around a recreational use would rank as a close second for
environmental value. A choice of either native plants or compatible
nursery varieties would still provide a significant environment
with both ecological as well as aesthetic merit.
A proposed postclosure land use following an initial vegetation
phase would influence plant selections more toward a vegetation
selection that would be less expensive to plant and remove. This
cover type would be less environmentally mitigative than the first
two options of natural parklands or native-or-non-native landscaped
recreation area.
A site that is strictly designed to comply with the regulatory
requirements of 27, CCR and Subtitle D regulations would employ the
simplest vegetation plan and would be the least costly to install
and maintain, while facilitating a visually pleasing cover. A
grassland type cover could still provide a satisfactory mitigative
result; if the site uses California native grasses and is located
within grassland or mixed open lands and forests (glade) or
savannah.
Vegetative restoration should be compatibly designed to fit in with
the surroundings. No radical selection of plants should be made
that will make the site stand out. It would not be prudent to place
a grove of tall Eucalyptus (non-natives) on an above ground
landfill in an open grassland environment. It is unnatural, a
non-native, and the unprotected stand of trees could be rendered
vulnerable to blow-down from strong winds over time, damaging the
final cover and creating added repair and cleanup costs.
Again,
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considerations must be exercised to fit the planting appearance and
the plant selections in with the surrounding environment.
Aesthetic Restorations
These mitigative projects provide a vegetative cover that supports
a plant community similar to surrounding native plant communities
but which derives its plant makeup more from nursery plant species.
The plant profile could employ trees, shrubs, and grasses assuming
similar ecological roles as their native counterparts. The final
result could range from natural appearing, to landscaped, both
cases presenting a visually satisfying product. A compromise form
would employ native plants, but with the landscaped
appearance.
Characteristics of an Aesthetic Restoration
• The use of non-native plants compatible with the environmental
conditions where they will be planted and/or use of native plants
when desired. This cover could assume natural plant profiles
(grasses, shrubs, and overstory trees) when appropriate.
• Application of landscape architectural techniques to create
natural- looking or purposely designed landscapes.
• Aesthetically pleasing landscapes that serve man’s needs or
requirements such as parks, golf courses, playing fields (baseball,
soccer) or recreation areas, and/or minimized visual impacts to the
surrounding community.
• Little potential for planned postclosure land use beyond the
initial planned use (although a secondary or tertiary postclosure
land use may not be ruled out).
Functional Sites
These landfill covers will have their primary function in ensuring
their compliance with the regulatory requirements of 27, CCR and
Subtitle D. This type of cover is the most commonly employed, using
a standard hydroseed mix of annual and/or perennial grasses. Some
smaller herbaceous plants such as legumes (vetch or lupine) may
also be used. Natural invasion and succession by nearby plant
species may play a role in the later years of postclosure
maintenance. Aesthetic or environmental mitigations would be of a
secondary importance in their design function.
Characteristics of a Functional Site
• The use of climatically compatible native or non-native plants in
the vegetative cover. No significant effort is expected in plant
community profiling. Possible use of grasses and planted or
volunteer plants such as small shrubs and, eventually trees, if the
cover can accommodate them.
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• Developing primarily engineered slopes and land features without
attempts at duplicating or mimicking surrounding land profiles or
aesthetic landscaping.
• Function takes precedence over form. The function of the final
cover design is to be in regulatory compliance. There would be
minimal land forming beyond required, engineered standards.
Functional requirements would include:
1. Slope stabilization.
2. Moisture control. a. Water penetration into cover. b. Down-slope
water flow control, drainage systems, etc. c. Leachate
control.
3. Reduced maintenance demand. a. Low irrigation requirements. b.
High reseeding characteristics or return seed replenishment. c.
Minimal maintenance or cleanup requirements. d. High potential for
postclosure use; the landscape materials are
“disposable” and can be easily removed should a future postclosure
use such as office buildings or warehouses be placed on the
site.
e. Minimum vegetation diversity. Grasses and possibly larger
herbaceous plants such as legumes.
Page 12
Chapter 4: Types of Vegetative Communities A “community” is defined
as “an aggregation of living organisms having mutual relationships
among themselves and to their environment.”2 A plant community
includes each element of the vegetation characterized by a dominant
species. For restoration of a plant community to be successfully
achieved for any project, an understanding of the basics of plant
communities must be explored. For a project proponent to install a
vegetation community that will have the highest chance of
succeeding, the planner must be aware of the types of plant
communities that exist throughout California and the one at his
project site. The operator must consider climate conditions, soil
types, and compositions in the project area and demonstrate an
awareness of the surface topography of the area surrounding the
project site where restoration will occur.
Even in using nursery stock instead of California native plant
stocks in a revegetation project, soil types, climate, and
equivalency in plant types are important to successful survival of
the final planting.
Throughout the State of California, plant communities have
developed and evolved into distinct assemblages of plants and
distribution patterns. Coastal plant communities differ greatly
from desert plant communities. Alpine conifer forests will differ
from valley chaparral. Species of plants will differ from one
northern oak woodland community in northern California versus a
southern oak woodland community in southern California, although
they may look superficially alike. Even the western coastal conifer
makeup is different from the conifer forests in the western
Sierras. An awareness of these subtle differences may help make the
difference in a restoration or revegetation project being a success
or a potential failure.
The Vegetative Zones California’s vegetative communities fall
within four major vegetative zones.3 (Micro- environments are found
within each major zone, containing their own distinctive plant
communities.) Following are the four major zones.
Coastal Zone
This vegetation zone embraces the majority of northern California
from Modoc County to the northeast, across the northern counties to
include the mountainous areas of Siskiyou, Shasta and Trinity
counties. This zone includes the coastal counties from Del Norte
south to San Diego County, bounded by the coastal ranges on its
eastern margin.
Plants in this zone are varieties that are highly moisture
dependent, preferring a more temperate average climate ranging from
the 50s (OF) to the 90s rarely. Rainfall is abundant to moderately
available while frequent occurrences of fog from the marine air
layer of the Pacific Ocean increase atmospheric moisture levels.
The conifers dominate the northern forests, including the
Redwoods
2 Munz, Phillip A. and David D. Keck, A California Flora and
Supplement, University of California Press, 1959, p. 11. 3 Duncan,
Craig Thomas, Guide to Vegetative Covers for California Landfills,
Bryan A. Stirrat and Associates, 1994.
Page 13
(Sequoia sempervirons) and Douglas Fir (Pseudotsuga menziesii).
These species dominate as the overstory species. Hardwoods (Western
Hemlock, oak, and others) can be commingled in some areas,
occupying the intermediate layer of vegetation.
Smaller shrubs fall in the understory at the closest to ground
level. More southerly forests will be populated with coastal
species of hardwood (deciduous) forests. A pocket of alpine desert
plant communities can be found in northern and eastern Siskiyou
County and Modoc County.
Interior Zone
The Interior Zone includes the entire Central Valley and a narrow
band that follows along the eastern slopes of the Coast Ranges,
including the west halves of Los Angeles, San Bernardino, Riverside
and San Diego counties. Climatic conditions in this zone are drier
than the Coastal Zone, being partially influenced by the initial
rain shadow effect of the Coast Ranges. Temperatures can vary from
the low 30s (OF) into the 100-plus degree range. Atmospheric
moisture is generally dry during the summer and fall months. A
short period of heavy rains occurs between September and
March.
This region is dominated by grasslands and Oak Chaparral
communities, often with higher concentrations of vegetation along
river and creek channels (riparian environments). Many of these
riparian environments are dominated by cottonwoods (Populus
trichocarpa or tremuloides) as well as willow (Salix subspecies) in
the overstory layer. Digger Pine (Pinus sabiniana) can be found in
the drier hilly areas of this zone. Embracing the San Gabriel and
San Bernardino Mountains, the Interior Zone holds distinctive
mountain plant communities in these ranges.
Mountain Zone
This zone includes the region running along the western slopes of
the Sierra Nevada, from southern Modoc County, across all western
Sierra counties southerly to Tehama County and including north Kern
County. Dry temperate to warm summers and cold, snowbound winters
at the higher elevations generally dominate climatic conditions in
the Mountain Zone.
The western Sierra receives high volumes of rain, and thunderstorms
are frequent. Much of the eastward migration of storm moisture
conveyed to this point is precipitated out before crossing to the
east desert regions. Vegetation in this area is dominated again by
conifers such as Ponderosa Pine (Pinus ponderosa) and Fir (Abies
grandis or A. concolor) in the overstory. These species of conifers
are more tolerant of dryer, hotter climates than the conifers of
the coastal varieties. Oak savannah or chaparral may dominate the
southern portion of this zone. Arid conditions may dominate in the
extreme southern zone. Hardwoods such as Valley Oaks (Quercus
lobata) are found more at the lower elevations and as intermediate
species at middle montane elevations.
Page 14
Desert Zone
The Desert Zone takes in northern Modoc County, the areas north of
Lake Tahoe, and all of the easternmost counties to the southern
California border. This zone includes the area bordered by the east
slopes of the Sierra Nevada. The climate in this zone ranges from
cool winter days to extremely hot summer daytime temperatures. The
climate is generally arid with relatively less snowfall than the
Mountain Region. Soil conditions are dry, sandy or stony, often
forming a “desert pavement,” creating harsh conditions for natural
plant growth. Precipitation is limited because of the rain shadow
of the Sierra. What rain there is may come primarily as cloudbursts
creating brief flash flood events. Vegetation in this region
consists of xerophytes—plants highly tolerant of harsh desert
conditions. Junipers (Juniperis) including J. californica and J.
communis in the north, and J. ostosperma in the Mojave region,
succulents, creosotes and other shrubs, and assorted species of
yuccas or other desert vegetation will dominate this plant
community.
The desert environment is particularly sensitive to impacts from
man. Desert regions, both low-altitude and alpine, possess very
subtle features difficult to replicate. These regions take a long
time to “heal“ after excavations have been performed, and the slow
rates of growth and relative sparseness of native plant species in
the desert region will reveal scarring longer than other impacted
areas. Barren rocky regions may make restoration nearly impossible
to achieve as desert pavement and the phenomenon of “desert
varnish,” a dark glaze over the rocky surfaces, are difficult to
reconstruct, requiring natural weathering to complete the process.
Alpine desert areas as in central Siskiyou county display subtle
signs of frost polygon-like forms in the soil, presenting cell-like
arrangements of surface stones, surrounding low hummocks over large
tracts of open grassland.
“Desert” refers to a natural environmental community created in
evolutionary response to hot arid climates. Desertification is an
environmental condition, usually resulting from the adverse
activities of man. These activities, such as mismanagement of
irrigation water, salt leaching, and concentration of other
minerals in the soil and wind erosion of soils from tilling
operations result from agricultural activities in fertile or
marginally fertile lands of the desert regions. In the arid soils,
chemicals accumulate and the soil surface forms a thin crust,
relatively impermeable to the sparse available rains of those
regions. The result is conditions that are hostile to plants and
animals and loss of natural soil nutrients that inhibits
revegetation efforts.
Page 15
Vegetative Zones
Page 16 Page 16
Chapter 5: Precipitation and Moisture The types of plants to be
selected and the irrigation plan intended for a specific landfill
site will depend upon the average natural precipitation in a
particular area. The project planner must take this variation into
consideration. The precipitation pattern of California is atypical
of most precipitation and climate distributions worldwide.
Most climate patterns follow defined responses to geographic
features, resulting in gradated changes across a climate regime.
This usually results in wetter coastal regions gradating to drier
or arid environments inland. In California, the association between
weather and precipitation, the widely varied terrain and regional
temperatures creates a far more intricate melange of environmental
zones. Precipitation may vary widely in two different areas even
though they may both be within the same vegetation zone and
geographic regime.
California’s terrain is divided lengthwise by two major mountain
chains running the length of the state. Two regional mountain
systems are located in the north central state and a long,
transverse range in southern California. The Central Valley
occupies the mid-portion of the state, while low desert and high
desert plateaus and mountain complexes occupy the northeast and
easternmost margins of California. The state’s length results in a
broad temperature range from the north latitudes to the south.
These wide-ranging environmental influences result in wide
variation in temperatures and precipitation, all within small
distances.
As an example, in the coastal vegetation zone, precipitation varies
from 10 inches average annually, southeast of Monterey, to 100
inches or more north of Eureka; a 90- inch difference. Temperatures
can be very cold on the north coast, yet warm in Monterey.
Precipitation in the Central Zone varies between 10 and 70 inches.
The eastern flank of the Sierra and the south desert region (Desert
Zone) range from 2 to 20 inches average annual precipitation.
A balance must be developed between the natural precipitation and
average temperatures, and the planned irrigation volumes for
landfill revegetation at a specific project site. (See Figure
2).
Page 17
\ I \~I ', __ /
of Active Landfills
Figure 3a
Distribution of California’s Landfills Californians live throughout
the state, in the most remote areas of the mountains, to the
farthest reaches of the desert. This distribution places these
sources of waste within virtually every climatic, temperature and
precipitation zone in the state. Figure 3a shows the locations of
the State’s 186 active landfills. This wide dispersal of landfills
demonstrates the diversity of waste management requirements and
postclosure maintenance and land use demands placed upon operators
and postclosure re-vegetation programs, both active and
proposed.
Page 19
Figure 3b shows 262 landfills, active and inactive, within
California. The majority of these landfills have not employed an
environmental restoration program. Most employ programs compliant
with regulations, employing the basic techniques of vegetative
cover and standard engineering practice. Many employ aesthetic
programs, incorporating golf courses or other recreational
facilities in the postclosure use plan.
Page 20
Chapter 6: Aspects of California’s Vegetation Plant Assemblage
Profiles
Just as plants develop associations based on climate, moisture, and
soil type, the plant community can establish itself into a simple
to complex interrelationship as a layered or stratified structure.
As the natural succession of a plant community develops through
time, the larger vegetation supersedes the previous pioneer plants.
Pioneer weeds and grasses begin the succession, preparing the soil
for the succeeding plants. The pioneer weeds and grasses are
eventually shaded out by larger shrubs. These shrubs are displaced
or dominated by the larger trees. This system of layering provides
environmental levels for wildlife and plants alike (Figure
4).
The main plant layers include the understory, intermediate, and
overstory layers.
Understory
This includes the smallest vegetation such as mosses, ferns,
grasses, small wildflowers, and low ground covering varieties of
herbaceous or woody plants.
Intermediate
This layer will include smaller and larger shrubs and smaller
species of trees or young saplings of larger overstory tree
species. These plants may be adapted to softer light and cooler
temperatures created by the shading effect of the overstory canopy.
Woody perennial plants dominate the intermediate story.
Overstory
This vegetative layer consists of the larger species of trees in
the natural assemblage. This layer can create a canopy that
influences the overall light availability and average temperatures
at the lower levels. These trees can be sparsely distributed or
closely growing together to create a tight canopy. Destruction of
the canopy trees can adversely affect the understory environment,
or provide a point of opportunity for saplings to fill in. Not
providing these trees in a poorly planned restoration project may
jeopardize the success of understory plant species growth and the
project.
A landfill revegetation or restoration project would shorten some
of this successional process, compressing the sequence into roughly
one step, with grasses, shrubs, and trees planted at the same time.
Invasive plants, including pest weeds, would impose on this plan if
a maintenance program to remove these invaders were not
exercised.
Page 21
Figure 4 Jacques Graber 1999
Plant Communities Within each of the four vegetation zones, plants
have established themselves into assemblages or communities. Each
community, when viewed as a whole, is an integrated system adapted
to that particular environment. Similar plant communities may be
found in the Coastal and the Mountain Zones, the Interior Zone as
well as the other zones. Though superficially resembling each other
in function, two similar looking plant communities will have
entirely different species assuming similar ecological functions.
Species aside, these vegetative communities follow several basic
patterns, such as grasslands, wetlands, woodlands or forests, etc.
Within these major patterns, though, is a whole spectrum of
variation. Some of the major plant assemblages most found in
California include4:
Valley Grassland and Savannah
This vegetation community consists primarily of annual or perennial
grasses with, now, predominantly introduced annual grass species
from Europe (Festuca and others), and annual or perennial
wildflowers. Grassland or prairie generally lacks
4 Munz and Keck, p. 11-18.
Page 22
major trees and shrubs. Though species such as oaks may be
dispersed throughout this community, they would generally not
constitute a “forest.”
Major streams or river channels that traverse grasslands or
prairies may support dense stands of hardwood trees and shrubs as
Riparian lands, being restricted to available water from the
stream. Grasslands and the remnants of a once expansive riparian
environment that existed along the major rivers and streams
dominate the Central Valley (Figure. 5a or b).
Coastal Prairie
Similar to prairie. Open temperate hill grasslands or glades, or
bald hills on the west slopes of the outer and middle coast ranges
in Mendocino and Trinity counties, north, and scattered to counties
southward to San Francisco County. In the past, native bunch
grasses and flowering herbs dominated coastal prairies. Because of
overgrazing, these native bunch grasses have been displaced by
annual grasses and by intrusion by non-native grasses.
Chaparral
This vegetation community consists frequently of an understory
grass soil cover with wildflowers within which are distributed, in
varying density, different species of shrubs and oaks or juniper as
intermediate and overstory plants. Chaparral is predominantly a dry
climate plant community. Many of the trees naturally found in this
environment possess thick corky bark (cork cambium) and are adapted
to the wildfires that raged through prior to human involvement.
These trees may include Interior Live Oak, Blue and White Oak,
Manzanita and chamise. This plant assemblage occupies areas along
Central Valley and foothills regions of California from Redding,
along the western Sierras. Chaparral can be found in the southern
California counties and along the eastern flanks of the Coast
Ranges from Redding to the San Bernardino Mountains, as well as
distributions south to San Diego County (Figure 5b).
Forest
These vegetation communities consist of a complex understory and
intermediate plant relationship, with high diversity in these
layers in natural mature forests. Woodlands’ overstory trees are
represented by two dominant tree types, conifers and deciduous,
with a mixture of the two as environmental conditions may dictate.
The dominant overstory trees will be made up of either species of
conifers in the higher altitudes or deciduous trees at lower
elevations. (Figure 5c).
Forest communities create the most impressive and oldest plant
communities in their natural mature state as exemplified by the
redwood and old growth forests of the northwest state, the Big
Trees National Forest in the central Sierra Nevada and the
Bristlecone Pines in the high Sierras. Conifers or deciduous
(broadleaf) trees can wholly dominate the overstory canopy to the
exclusion of the other, or they can share this niche in varying
proportions depending upon climate, elevation and soil conditions.
Forest or Woodlands command the Coastal and Mountain Zones as well
as the riparian environments in the Central Valley.
Page 23
Several divisions of the forest community are listed here. Forest
communities are characterized by the dominant conifer found in each
of them:
Closed Cone Pine Forest. This community is found at intermittent
locations along the California coast from Mendocino to Santa
Barbara counties.
Redwood Forest. Located along the west slopes of the Coast Range
from Del Norte to Santa Cruz counties. Some small areas are found
in Monterey County.
Douglas Fir Forest. This community is found in the north Coast
Ranges from Mendocino County southward, with scattered remnants to
Sonoma and Marin Counties, easterly of the redwood forest
regions.
Yellow Pine Forest. Found in the North Coast regions, to Southern
California.
Red Fir Forest. Found in the North Coast ranges to Southern
California.
Lodgepole Forest. Found in northernmost California to the central
Sierra.
Northern Juniper Woodland. A variant of woodland community in which
the dominant tree species is Juniper (Juniperus occidentalis). This
community can be found in central Siskiyou County, easterly to
Modoc County and south to Mono County.
Desert or Arid
This plant assemblage will be found in those areas of California
where moisture and temperature are at their extremes. Soil
conditions are harsh and difficult for plants to grow in. The
dominant plants, known as Xerophytes are deep-rooted, and
slow-growing. Many plants in the desert community are defensive;
producing terpines that will keep invasive plants away from their
roots; blocking competition for valuable water. Leaves are thick
and physical defenses such as spines, thorns, and foul-tasting
resins keep herbivorous animals from destroying their slow-growing
foliage. Knowledge of these traits can help in planning desert
restoration projects, so as not to put these highly competitive
plant species too close to each other. Alkali sink vegetation is
found in poorly drained alkali flats and playas on the floor of the
Central Valley and arid regions on the east slopes of the Sierra
Nevada. (Figure 6a).
Wetland or Estuarine, Riparian, and Vernal Pools
These three aquatic plant communities constitute the vegetation
assemblages found along natural water bodies throughout California.
Some are extremely small and fragile, such as vernal pools, their
combined statewide total areas barely covering several acres.
Plants in these communities are highly moisture-dependent, yet they
can be adapted to intermittent dry cycles, going into dormancy.
Many of these species are microscopic and may be sensitive and
vulnerable to minor changes in their conditions. They can also
serve as effective bioremediation mechanisms, filtering out certain
effluent components in sewage treatment projects (Figure 6b,
c).
Page 24
Wetland or Estuarine. These plant communities include Coastal Salt
Marsh and Freshwater Marsh. They can be found generally as
bordering lands along bays (large or small) salt, and fresh water
bodies, lakes and rivers. The largest single wetland environment in
California can be found at the north shore of Suisun Bay northeast
of San Francisco. This plant community can consist of vast expanses
of rushes and grasses adapted to live in water- saturated soils and
conditions of brackish to fresh water. Floating plants, including
an introduced species of water hyacinth, can be found in areas of
the Sacramento and San Joaquin River Delta. Sloughs, lagoons, or
river channels are generally associated with the wetland or
estuarine community. Many estuarine or wetland systems can be
influenced by tidal conditions (Figure 6b, c).
Riparian. The riparian environment is an ecologic community
including plants growing along an established stream or river
channel and the floodplain associated with it. Riparian vegetation
consists of rapidly growing, moisture dependent species such as
poplars or willows, assorted thick-growing shrubs, vines and
understory grasses or other smaller plants. The riparian
environment can form a complex multi-layered vegetation community.
Dense forests of deciduous trees, understory shrubs and grasses can
occupy areas embracing the stream channel while small wetland
environments may be interspersed along the river or stream.
Early in California’s history, the riparian environment dominated
the Central Valley where flooding along the Sacramento River
floodplain was uncontrolled and frequent. Since western man’s
immigration to California began, approximately 98 percent of this
vegetation community had been destroyed by flood control programs,
and by agriculture and other development.
Vernal Pools. Endemic to California, the vernal pool is one of the
smallest environments, and one of the most sensitive to damaging
impacts. The vernal pool plays an elusive role in project
development and restoration issues. The discussion of what
constitutes a “vernal pool” has caused some debate and legal
consternation among developers and environmentalists. The ultimate
indicator of what constitutes a vernal pool is the presence of
certain plants that are restricted locally or entirely by this type
of habitat.5
The vernal pool vegetation community can be very small in scale. A
vernal pool is a water body often only several dozens of square
feet in area and only inches deep. Vernal pools are seasonally
created when water collects in a natural surface depression that is
rendered water retentive by hardpan, claypan, or other low porosity
soils in the basin. The vernal pool is intermittent, evaporating
several days or weeks after it reaches its fullest level. This
characteristic makes defining it even more confusing. The vegetal
assemblage can consist of very small species of grasses, mosses,
and some associated trees and/or shrubs.
5 Pritchett, David A., ”Creation and Monitoring of Vernal Pools at
Santa Barbara, California. ” See references in bibliography.”
Page 25
Some rare or endangered species of vernal pool life such as fairy
shrimp are found on the macroscopic and the microscopic level.
(Figure 6c). Many vernal pool inhabitants often hibernate during
the dry seasonal cycles. Vernal pools create issue for their often
being located on prime lands for development and for being
temporary or “insignificant” causing debate over their importance
both in their destruction as well as their mitigative significance.
On the other hand, vernal pool “construction” can be a mitigative
opportunity for a project proponent, as vernal pools are small yet
often of environmental significance.
Compatible Plant Associations When a closure project features a
golf course, business park, or recreational park, the operator may
select nursery rather than native plants for the landscaping.
Selection of plant communities for such projects would be based
upon the dominant geographic, soils, and climatic characteristics
in which the project is located. These conditions would then
determine the dominant plant types used. The main difference is
that the plants that are selected would not be California native
species, but they would still be compatible with the environmental
characteristics of the site to ensure survival.
This type of planting program may require a more intensive
maintenance regimen to control invasive plant species, pests,
irrigation, and nutrient provision. Using plant volunteerism by
neighboring native species to stock the site would not be employed
to avoid competition with the introduced plants. If an aggressive
plant control program is not followed, invasive (volunteer) plants
could still establish themselves. Using the natural
overstory-understory distribution concept could be applied to
cultivated non-native planting.
Page 26
- Grassland or Prairie - Figure Sa
~~,Cl.'\1flllM&AIJlt\'!Wll\ftl/W~'Mli~~~-JhJ~JIOi'AJIO'JOI\M/U~'L\118~!1D~Jla!Mll!M'Ol\ttlJ1~1\0Uall~l\tlllJla@!M'rtlill
- Chaparral - Grass with Valley Oaks or Juniper
or other dominant hardwood trees
Figure Sb
Mature Woodland With Ove rsto ry Trees and Understory shrubs
Hardwood. Conifer. or mixed populations
Figure Sc
Shrubs. Succulents. Grasses. Trees adapted for dry desert
environment.
Figure 6a ~.~ -~
-=--"' ~~----....:::::!'?~~~~-, ,.-.:::·:b --........,.._ ~ --', .-
- ···-· Wetlands or Estuarine
Water saturated soil. reeds. rushes. aquatic plants (hyacinth.
etc.) some trees may be present
salt brackish or fresh water
Vernal Pool Commonly shallow result from
water collection on hard pan substrate.
Can be intermittant
Pioneer Grasses Small Shrubs Soft Hardwoods Weeds (Poplar,
Willow)
Expanding Saplings
Figure 9
Mature Hardwoods
Page 29
Chapter 7: Landfill Vegetative Design As a landfill approaches its
waning years of active use, the operator should consider the
details of the final closure and postclosure land use planning for
the facility. At this time, the operator must consider if the
closure will include an integrated planned postclosure use such as
creating undeveloped land, a park, a playing field or preserve,
golf course, business park, or industrial park. These “uses” will
make a difference in the planned final cover design and possible
slope design or contouring design for the decks and side slopes,
irrigation, and drainage control. The more complex or structured
the final land use, the more complex will be the design
requirements for the final cover and revegetation planning. An
undeveloped, open grassland will demand less from the final cover
design than a planned recreational park or a business park. The
final cover planning will be dictated by other conditions such as
the final cover and moisture layer components, physical aspects of
the landfill site, and the surrounding environments.
Costs and availability of materials such as soil and plant stocks
will dictate the proposed design characteristics. The elements to
consider in the restoration or other final closure plan will
include landfill design and additional uses for vegetative
cover.
Landfill Design Considerations Proposed Postclosure Use
If there is an actual planned postclosure use or idea in mind for
the site, this aspect will have to be analyzed prior to any actual
design planning of the final cover. Different uses will impact the
demands placed on the final cover, including its thickness, slope
profiles, and, in considering revegetation or restoration projects,
the quality and quantity of the vegetative layer soil that will be
utilized.
Drainage and supplemental irrigation issues will have to be
addressed. If the final plan is to install a simple grass cover on
the landfill, a thin vegetative layer that is in compliance with
the regulations (Title 27 or Subtitle D) may be all that is
necessary. If more complex plantings are proposed, berms,
supplemental soils on benches and other such enhancements to the
vegetative layer may be required to support deeper-rooted plants
and to protect the underlying moisture barrier from root
penetration.
Some final closure plans are proposing the use of a monolithic
cover instead of the current multi-layer design in use on most
landfills. The monolithic cover proposals use a thicker, single
soil layer that would provide sufficient depths to include
deep-rooted vegetative plantings. One proposed plan incorporates
moisture control elements into the monolithic cover by using
poplars or other similar vegetation and a groundcover plant such as
clover to wick off soil moisture by evapotranspiration.6
Whether planning for root depths to determine the vegetative cover
thickness or planning root depths to best work with the planned
soil thickness, either technique requires forethought in designing
the cover and vegetative systems as a unit.
6 Lich, Lewis, Mark Madison and Alicia Lanier, Ecolotree and CH2M
Hill, “Poplar Tree Technology Provides Cost and Management
Advantage for Landfills,” October 1996.
Page 31
Development of contours of the final cover can be impacted by the
final postclosure use. An operator who intends to create a
restoration project may create more naturally compatible slopes and
contours to the adjacent landscape. Or, the operator may require
basic contours in compliance with current regulations and the
engineering needs of the final project.
Natural Parks, Preserves, and Mitigation Sites. These uses require
“permanent cover” of native plants that will not be displaced for a
future land use such as a business park or other structures.
Recreational parks and golf courses. These uses will entail
permanent or long-term post-closure use cover elements. These sites
can be developed with “disposable” cover. The vegetation may
usually be nursery plantings, though natural plant species are
optional. A potential for their removal exists, allowing re-use of
the site for a business park or other structured development at a
later time.
Final Design of the Landfill
This will dictate what kind of planting and vegetative layer
conditions will be placed on the landfill final cover. Steep slopes
on final cover will require more aggressively rooted vegetative
types than shallow slopes. Benches can provide planting areas for
deep-rooted plants. These benches must be sufficiently wide to
accommodate maintenance vehicles in addition to the proposed
plantings such as trees or large shrubs. A thin vegetative cover
will restrict plant options to shallow-rooted varieties that will
not penetrate moisture barrier layers. Irrigation from natural
rainfall will dictate the types of vegetation available for use in
dry or moist conditions. This may require supplemental irrigation
to support the desired vegetative cover, at least until the plants
are strongly established. Slopes and naturalized contours can
provide alternative planning options for revegetation projects with
areas to enhance opportunities for vegetation planting.
Benches. Benches can provide deep soil zones for trees if they are
wide enough to provide space for the vegetation and maintenance
activities, usually with the vegetation at the outside edge of the
bench, where soil is deepest. Grouping trees instead of lining them
up creates more natural “groves.”
Decks. If top layers of vegetative soil are sufficiently supplied
beyond the minimum 12-inch requirement (preferably 48 inches or
more), larger plants with deeper roots can be supported.
Berms. Berms add small areas of thicker vegetative soils as hills
or other raised land features (48 inches or more); the added soil
can provide sufficient depths for trees or large shrubs to enhance
the natural vegetative appearances of the final cover.
Advanced planning of the landfill, taking the postclosure land use
into account at the very outset, can help the operator plan for
adequate soil and topsoil supplies for the final cover. By planning
the final elevations and contours of the cover layer in advance,
the underlying waste volume can be graded to within more precise
tolerances to conform to the projected design.
Page 32
By designing the waste contours to closely match the finished
design specifications, less financial resource is expended on poor
grade foundation soil built to grade and, instead, can be used more
efficiently in providing greater volumes of adequate quality
topsoil in the vegetative layer. This could result in additional
capital for other closure project costs or savings to the operator
overall. (Figure 7 a and b).
Jacques Graber 1999
Figure 7a. A landfill with wastes that are not closely configured
to the planned final contours will require additional foundation
soil to achieve design grades. Less funding will be available for
the acquisition of useful fertile topsoil for the vegetation
layer.
Figure 7b. A landfill with wastes more closely configured to
planned final contours will require less foundation layer soil to
achieve grade. This allows for more funding to be allocated toward
better quality, thicker topsoil for the vegetative layer. A thicker
topsoil layer will allow for more vegetation design options and
improve chances for plant survival.
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Location of Landfill
Where the landfill is located will influence the type of vegetation
that can be used on it. Landfills in hot, dry regions will support
appropriately selected vegetation for those climates. Irrigation
can provide added options for vegetation selection, but it is more
expensive to include as a planned element in vegetation selection
and closure maintenance plans. In addition, atmospheric conditions
can affect plant choices. Revegetation in urban areas may pose a
challenge because airborne pollutants can adversely affect some
vegetation. Conifers in the Los Angeles basin and grape plants in
the Central Valley have demonstrated this sensitivity by loss of
foliage and higher mortality.
General wind conditions at site should be considered when designing
a vegetation cover. Pollutant gases can collect in windward-facing
valleys or pockets, creating adverse atmospheric conditions
injurious to plants.
Excessively tall trees may prove vulnerable to blow-down
(“wind-throw”) if left unprotected. This can cause damage to the
final cover, should the roots peel the soil layer up with the
toppled tree. Natural, established tree groves in areas with a
prevailing wind tend to develop an airfoil-like profile, due to
natural pruning. Smaller trees of the expanding grove tend to grow
at the perimeter of the grove with larger, mature trees in the
center area of the grove. This dome-like form encourages airflow
gradually over and around the tree grove (Figure 8a). Single- line
hedgerow-like plantings or isolated individuals, especially at the
edges of top decks and maintenance roads or benches, place adult
trees in a vulnerable position to strong winds, encouraging
wind-throw (Figure 8b). Planting shorter trees at the perimeter of
a grove around taller varieties or adult trees can provide a
windbreak by slowing wind velocities and directing airflow over or
around the taller canopy layer.
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Plant Community
When a vegetative cover is installed, extensive planning must be
exercised in laying out the details of the vegetative layer and the
final plantings. This can be most complex when all vegetation is
planned at the initial planting. A strategy for interim maintenance
must still be instituted when the natural population process of a
vegetative cover is attempted. A planned vegetative community can
be designed and installed in a variety of ways, with three
suggestions as follows:
Developing and providing all of the major elements of the plant
community, such as grasses, shrubs and trees, at the very outset of
planting.
This procedure will require the most advanced planning but it
should provide the greatest element of control in the overall plant
community design and final outcome. The final plant community would
be established and maturing early in the revegetation, and
postclosure maintenance program. Some invasive volunteerism by
outside plants could occur if the operator does not exercise
aggressive control efforts by keeping them out. The initial
hydroseeding of annual grasses, or hand planting of native
perennial grasses can be introduced for slope stabilization with
larger plants installed at later dates.
Providing the proper environment and soil conditions to encourage
plant growth and allowing natural invasion (volunteering) by native
plants adjacent to the site.
This procedure provides the lowest element of control on the types
of plants that may be introduced to the site. This process is the
most dependent upon the unpredictable phenomenon of natural plant
establishment and succession that may take longer than the
immediate planting procedure. Some sort of initial soil
stabilization planting with a rapid growing annual and/or perennial
grass or ground cover will still be required to prevent erosion of
the soil cap. The plant succession process occurs as the selected
area matures.
Naturally, the pioneer plants, most adapted to the harsh conditions
of bare, usually poor quality soils, begin the process. This
community usually consists of low growing or prostrate weeds and
grasses with deep taproots. This initial plant association begins
the soil nutrient construction and softening of the soil that
provides the conditions more conducive to the later succeeding
plants to establish themselves.
As the soil is broken up and softened, taller grasses gain a
foothold and establish themselves. In time, legumes, herbaceous
perennials and woody perennials can begin the larger plant
occupation as soil quality and nutrient content improves.
Eventually, shrubs and the larger trees assume the mature level on
the location.
A landfill preferably will have an annual and perennial native
grass planting in its earliest vegetation phase, which may skip the
pioneer phase of the succession. Some stronger invasive weeds may
still try to occupy the site.
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Shrubs may not be allowed on the site to avoid root penetration,
but after the postclosure maintenance program is complete, shrubs
and trees may complete the progression anyway (Figure 9).
Combining planned planting with volunteering by adjacent native
species to create the final vegetation cover.
This technique can allow some control in the selection and
establishment of the larger plants with other plant selections and
distributions left to chance. Efforts may still be required to
control undesired pest plant intrusion, especially plants with deep
reaching taproots that could damage the moisture barrier.
Jacques Graber 1999
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Additional Uses for Vegetative Cover In addition to the obvious
uses of vegetative cover that include regulatory compliance, soil
stabilization and aesthetic contribution to the landfill site,
vegetative cover has some specialized functions that can be used to
advantage.
Bioremediation
Vegetative cover can be used in certain situations to attenuate
concentrations of certain chemicals, salts, trace metals, and other
toxic materials such as boron and selenium present in soils.
Certain grasses have the capacity of surviving in higher
concentrations of these compounds than other vegetation candidates.
In addition these plants tend to store these compounds in their
leaf and stem tissues while removing them from the soil. This
process can be used to advantage to prepare contaminated soils at
problem sites for future population with less tolerant plants. By
planting with these salt-tolerant species and mowing them at
maturity, the contaminants can be removed. The contaminated
cuttings are disposed at a different, appropriate disposal site as
fill. After repeated cycles, the salts are removed from the soil;
the less tolerant vegetation selections can be planted.
A pilot project at Mountain View Sanitary district wastewater
treatment facility employed conifer trees as a moisture exchanging
evapotranspiration mechanism to process water. The trees transpire
the water into the atmosphere, and create a harvestable revenue
crop at maturity. This activity can provide a year-round operation
as a serviceable alternative to conventional irrigation disposal
systems that shut down during the winter months. This technique
could be employed at landfill sludge or septage ponds or possibly
leachate ponds, upon closure.
Cattails and similar estuarine plants can absorb certain materials
in solution, utilizing them as nutrients. Where high concentrations
of these substances in water from sludge or leachate could pose
pollution problems such as in leachate and certain liquid waste
ponds, cattails and related water plants can mitigate these
situations. With naturalized leachate ponds and cattails or similar
rushes, natural looking artificial “wetlands” could be created. The
cleaned water from these ponds can be recycled as irrigation water
after additional treatment. The City of Arcata, in Humboldt County,
is employing this technique at the final stages of its wastewater
treatment process.
Landfill Gas
Remediation of landfill gas and detection of landfill gas can be
accomplished using surface vegetation. Some landfill gas in low
concentrations in soil can be absorbed and attenuated by the
nitrogen fixing properties of certain legumes and other plant
species that possess such bacteria or fungi in their roots. If gas
concentrations do become excessive, plants are sensitive to these
gases and their abnormal appearance, loss of leaves, usually will
alert the operator to a potential gas problem that will need
attention. This condition must be responded to quickly before
permanent damage is caused to the impacted vegetation, or the gas
migrates and spreads further from the initial site.
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Extreme exposures of vegetation to high gas concentrations can lead
to stunting of growth or defoliation in some instances, or plant
death, requiring subsequent removal and replanting.
Leachates
Leachates that develop at a landfill and accumulate in areas
shallow enough to impact plant roots can be detected by plants.
Loss of leaves and die-off of vegetation on or in close proximity
to the landfill site may indicate signs of a possible leachate
problem. With the right conditions and leachate composition,
bioremediation (see above) can be employed to reduce leachate
impacts.
Remediation of Nitrogen Deficiency
Certain plant groups, the legumes particularly, have a natural
ability, through nitrogen-fixing fungal symbiotes, to fix nitrogen
in the soil. This nitrogen-fixing ability aids in improving the
nutrient quality of the soil that will encourage other plants to
grow.
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Chapter 8: Considerations in Vegetation Selection Prior to
initiating a vegetation or restoration project, several criteria
must be considered in selecting the plants that will be utilized in
the final vegetation population.
Site-Specific Considerations Soil Characteristics
The plant assemblage to be selected must be compatible with the
soils that will be placed as the vegetative layer. Most soils that
are utilized for vegetative cover are generally not the original
native topsoils and may not be quality topsoils, lacking the
primary nutrients found in natural topsoils.
Borrow Soils
Borrow soils may require amendments. This can be accomplished by
adding mulch or wood waste material that has been properly
processed and sorted, to the soil. Soil chemistry may be considered
to anticipate potential problems with trace chemicals or salts.
Relatively sterile soils may require augmentation with fertilizers,
and compost to satisfy plant growth needs. Stockpiling the original
topsoil layer until the project is done is a sound plan; replacing
it on the cap upon completion.
Soil compaction may be an additional consideration in providing the
optimum soil conditions for vegetative cover. If soil is compacted
excessively, this will inhibit root development of the vegetation.
Some grasses can serve as soil softeners, which can allow
succeeding vegetation to establish itself.
Moisture or Irrigation Requirements
When a landfill is closed, the final layers of cover material may
include a clay or geomembrane layer in the moisture barrier. Often,
when this clay layer is utilized, irrigation or soil moistening
must be designed to maintain required moisture levels in the soil
to safeguard against desiccation of the clay layer. This moistening
activity will be conditioned upon the annual precipitation and
climate of each individual site. The moistening function can be
taken advantage of as a means to support vegetative cover that may
be planted on the final cover. The moisture level must be designed
to account for the climate of the site location including annual
rainfall volumes and periods of occurrences, the type of clay
material to be utilized in the barrier, and the planned plant
community to be installed on the landfill site. Once these
conditions are established, the volume of water required for proper
moisture control can be determined. Water Use Classification of
Landscape Species (WUCOLS) is a reference published by the
University of California Cooperative Extension that discusses all
of the parameters involved in designing a vegetation cover.
If artificial irrigation is planned for the site, the source water
must be tested for contaminants and the chemical constituents in
the planned water must be considered. The chemical constituents in
some water may include salts and other
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trace materials that may accumulate in the irrigated soil which can
cause salt or chemical buildup leading to plant damage or
mortality. A project planned to employ irrigation water from a
cooling plant was designed for a Southern California landfill.7 In
time, the vegetation on the irrigated landfill site began dying. A
study of the source water revealed high concentrations of boron and
other dissolved substances. These salts were injuring the
vegetation being irrigated on the landfill. To correct the problem,
plans are being developed to process the effluent water from the
power plant to remove these salts prior to irrigation.
In addition to moisture being introduced, control of drainage off
site must also be properly designed. Some sites may require less
artificial irrigation with more surface runoff facilities provided
at the site than other locations.
Maintenance Requirements
Maintenance of the final cover and its accompanying vegetation can
be influenced by the proper design steps taken in constructing the
vegetative layer. Selection of slow-growing plants will reduce the
numbers of times maintenance crews may be needed to thin or control
growth of grasses or other foliage. Selecting clean plants will
help in cutting cleanup costs.
Some trees such as eucalyptus are extreme generators of litter.
They produce an abundance of debris from fallen branches, topping
from high winds during storms, bark debris, a hard nut-like seed
pod and the thick lignin rich leaves that do not decompose readily.
Vegetation that produces such volumes of litter can require more
frequent cleanup maintenance than most native plants require. In
addition to the cleanup requirements, unmaintained litter buildup
of this kind can pose a potential fire hazard that could present
added emergency costs for fighting a fire. The high oil content in
eucalyptus, in addition, creates hot fires.
Native plants especially adapted to the environmental conditions of
the candidate project site can reduce irrigation requirements as
well as maintenance and pest control. Native plants are adapted to
defend themselves from indigenous pests.
These plants can possess defense mechanisms effective against
native plant pests. Using native plants in final cover planting
should only increase the chances of plant survival. This can help
in reducing costs of cleanup and replacement of plants lost to pest
infestations.
Plant Compatibility
Plants in their natural assemblages have formed compatible
community associations. Some plants have special defenses, usually
chemical, to promote their survival. Attempting to place
competitive vegetation too close to such defensive varieties will
reduce the chances of survival of the “invasive” plant. Usually the
protective zone of a plant will extend to the edge of its drip
zone; the area directly below the crown of the tree or bush.
Eucalyptus (non-native), oaks, and California Bay (native) are some
potent defenders of their root zones.
7 Class I Conceptual Landscape Plan, BKK Class I Landfill, West
Covina, CA, 1996
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Climbing plants should be avoided because they can overpower the
supporting tree they may establish in, by blocking the sunlight to
the leaves. Certain California varieties of wild grapes can overrun
a large tree in a matter of a few years.
Plant Chemical Products
An awareness of the chemical by-products plants produce (such as
terpines) can help in determining the data that may be generated
during water quality and soil quality analyses. Decomposing leaf
detritus or bark debris can accumulate in the soil and percolate
out as complex compounds that can mimic certain manmade
hydrocarbons or leachate compounds. This can confuse data sampling
and source determination. Eucalyptus, California Bay, and most
conifers produce high concentrations of these chemicals. An
understanding of this can reduce confusion when data sampling shows
unusually high readings of hydrocarbons. The use of chips from
these trees as wood wastes or soil amendments can create the same
effects, leaving dissolved terpines in the soil.
Native versus introduced (non-native) plants. The role of the
vegetative cover is to stabilize landfill slopes, mitigate or
control moisture levels in the soil, control surface runoff and
comply with regulatory requirements. The landfill designer must
also realize that this cover will continue as a long-term impact on
the environment (hopefully beneficial). The landfill cover also
should ideally serve as a repair to the environment. When possible,
the vegetation should provide a near reconstruction of the
ecosystem that the landfill had displaced, providing the native
plant makeup to maintain the plant and wildlife diversity remaining
in California. A vegetative assemblage that most completely
integrates itself with the surrounding environment under given
circumstances is what an operator who is attempting restoration is
trying to achieve. A natural restoration would be the ideal result
for the vegetative cover project; providing renewed natural
environments for future generations. A landscape planner must
consider several things in the overall look of the plant
cover.
Planting Considerations Plant Heights
When designing the final plant distribution, will the vegetation
compliment or blend in with the surrounding vegetation and
environment? Can it at least present an acceptable appearance? A
landfill in open grassland with 40-foot tall trees would present an
obvious visual impact inconsistent with the natural surroundings,
focusing attention on the landfill r