Construction practices have a potentially greater
influence on a DOT's ongoing maintenance situation
regarding vegetation management, than any other
part of the organization.
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| 4.10.1
General Weed Prevention Practices for Site-Disturbing
Projects in Construction |
|
In general
- A noxious weed abatement program should be implemented:
- Construction equipment should be steam-cleaned
and inspected to ensure that it arrives on site
free of mud and seed-bearing material.
- Seeds and straw material should be certified
as weed-free.
- Areas of noxious weeds should be identified and
treated prior to construction.
- In situations where mechanical controls are
not enough, the application of fertilizers and the
use of herbicides to suppress undesirable competing
species may be necessary. Herbicides can eliminate
undesirable species more reliably, but they may eliminate
desirable species. Their use near watercourses may
also be severely curtailed by local, state, and federal
permit requirements. Several herbicides are approved
for near-stream use and degrade quickly, but their
use should be considered a last resort and the effects
of excessive spray or overspray carefully controlled.
If herbicide use is both advisable and permitted,
the specific choice should be based first on whether
the herbicide is absorbed by the leaves or by the
roots (e.g., Jacoby 1987).[N]
The most common foliar-absorbed herbicide is 2,4-D,
manufactured by numerous companies and particularly
effective on broadleaf weeds and some shrubs. Other
foliar herbicides have become available more recently
and are commonly mixed with 2,4-D for broad-spectrum
control. Root-absorbed herbicides are either sprayed
(commonly mixed with dye to show the area of application)
or spread in granular form. They persist longer than
most foliar herbicides, and some are formulated to
kill newly sprouted weeds for some time after application.
- Areas treated to remove noxious weeds should
be revegetated with appropriate native species.
The following weed prevention practices for construction
projects and maintenance programs are synthesized from
practices recommended by NYSDOT [N]
and the U.S. Forest Service [N],
two of the more complete sets of practices offered
by managers of linear corridors in the U.S.
- Provide tools for inspection/enforcement/results by
incorporating, as appropriate, standard specifications,
special specifications, notes and special notes as
described in the previous section.
- Identification, awareness, and education – Once
you know which invasive species are a priority in
your area, learn to identify these plants. Improve
effectiveness of prevention practices through weed
awareness and education.
- Provide information, training and appropriate
weed identification materials to people potentially
involved in weed introduction, establishment, and
spread on agency lands, including agency managers,
employees, contract workers, permit holders, and
recreational visitors. Educate them to an appropriate
level in weed identification, biology, impacts, and
effective prevention measures.
- Provide proficient weed management expertise at
each administrative unit. Expertise means that necessary
skills are available and corporate knowledge is maintained.
- Develop incentive programs encouraging weed awareness
detection, reporting, and for locating new invaders.
- During Project Construction Phase, ensure that
provisions for location, prevention and control of
invasive species are understood by Department Construction
staff and Contractor staff prior to construction
and implemented throughout the project. Invasive
species considerations should be routinely addressed
by Department staff to Contractor staff during pre-bid,
pre-construction, get-start and weekly safety meetings,
as appropriate.
- Inventory – Developing an inventory
of the priority invasive plants on your site or in
your management area is important for several reasons.
First and foremost, knowing where the invasive plants
live is essential to control efforts; by definition,
the species will continue to exist and spread until
they are controlled. Finally, since new invaders can
show-up at any time and are easiest to control when
they first arise in an area, regular checking of the
site(s) and updating of the inventory is important.
- Before ground-disturbing activities begin, inventory
and prioritize weed infestations for treatment in
project operating areas and along access routes.
- Identify what weeds are on site, or within reasonably
expected potential invasion vicinity, and do a risk
assessment accordingly.
- Any additional priority invasive species populations
encountered within the project area during construction
should be noted and if invasive species within the
project limits are not adequately controlled, the
Regional Maintenance Engineer should be notified
immediately so that controls can be addressed post
construction.
- To assist with future control efforts, during
the Operation and Maintenance of all elements of
the state transportation system, the agency shall
initiate a system and Regions are encouraged to formally
identify and inventory priority invasive species
known to exist along the roadside within and immediately
adjacent to the ROW. Due to their heightened role
in the introduction and spread of invasive species,
priority areas to initiate invasive species inventory
efforts shall be the interstate, expressway and parkway
systems, as practical. Additional priority species
and inventory locations may develop as the result
of Region-wide planning efforts and should also be
considered. This inventory should also provide information
regarding the extent of invasive species populations
adjacent to and outside the ROW. Identified priority
invasive species will be considered and managed as
appropriate to: (1) limit additional introduction
of invasive species; (2) limit the further spread
of invasive species; and (3) eradicate or control
existing invasive species populations.
- Incorporate weed prevention and control into
project layout, design, alternative evaluation, and
project decisions.
- For the site or maintenance program in question,
assess weed risks, analyze potential treatment of
high-risk sites for weed establishment and spread,
and identify prevention practices.
- Determine prevention and maintenance needs, to
include the use of herbicides, if needed, at the
onset of project planning.
- Control weeds as necessary.
- Begin project operations in uninfested areas before
operating in weed-infested areas.
- Locate and use weed-free project staging areas.
- Avoid or minimize all types of travel through
weed- infested areas, or restrict to those periods
when spread of seed or propagules are least likely.
- Coordinate project activities with any nearby
herbicide application to maximize cost effectiveness
of weed treatments.
- Evaluate options, including closure, to regulate
the flow of traffic on sites where desired vegetation
needs to be established. Sites could include road
and trail rights-of-way, and other areas of disturbed
soils.
- Minimize Soil Disturbance – Due to
the nature of invasive plants to rapidly colonize
areas of disturbed soil, out-compete native species
and become firmly established very quickly, it is
essential to minimize areas of soil disturbance.
- In those vegetation types with relatively closed
canopies, retain shade to the extent possible to
suppress weeds and prevent their establishment and
growth.
- Avoid creating soil conditions that promote weed
germination and establishment.
- Minimize soil disturbance to the extent practical,
consistent with project objectives.
- Materials Sources - Prevent the introduction
and spread of weeds caused by moving infested sand,
gravel, borrow, and fill material by inspect material
sources on site, and ensure that they are weed- free
before use and transport. Treat weed-infested sources
for eradication, and strip and stockpile contaminated
material before any use of pit material.
- Inspect and document the area where material from
treated weed- infested sources is used, annually
for at least three years after project completion,
to ensure that any weeds transported to the site
are promptly detected and controlled.
- Maintain stockpiled, uninfested material in a
weed-free condition.
- Avoid or remove sources of weed seed and propagules
to prevent new weed infestations and the spread of
existing weeds.
- Temporary Erosion and Sediment Control – DOT
policy requires sound temporary erosion and sediment
control practices on all projects that disturb soil.
This practice is particularly important in preventing
the introduction and continued spread of invasive
plant species. Where invasive species are known to
exist, rapid and diligent erosion and sediment control,
is particularly important.
- Mulch – Due to the nature of invasive
plants to rapidly colonize any area of disturbed soil,
it is essential that all disturbed areas be mulched
and seeded as soon as possible. If outside the growing
season for seed germination, disturbed sites should
still be mulched. Sources of mulch should be free
of invasive plant parts or seeds. Use of straw or
wood fiber mulch is preferred. If hay mulch is used,
it should be verified as originating from an invasive
free source.
- Early Detection and Rapid Response – Invasive
species, by their nature, spread very rapidly once
introduced to a new area. Therefore it is essential
that new infestations be identified and controlled
as quickly as possible. Control practices for small
populations are far more likely to succeed, are significantly
less expensive, and provide more options for control
methodology.
- Rapid Revegetation - Although not a specific
condition, replanting or reseeding with native species
is highly desired. All of the control methods below
are aimed at reducing or eliminating invasive species
so that natives are encouraged to grow and re-establish
stable conditions that are not conducive to invasive
colonization. In most cases removal or reduction of
invasive populations will be enough to release native
species and re-establish their dominance on a site.
Replanting may be desirable on private lands where
it can be used as a quid pro quo with the landowner
for permission to remove invasive plants. Where project
disturbance creates bare ground, consistent with project
objectives, reestablish vegetation to prevent conditions
to establish weeds.
- Revegetate disturbed soil (except travelways on
surfaced projects) in a manner that optimizes plant
establishment for that specific site. Define for
each project what constitutes disturbed soil and
objectives for plant cover revegetation.
- Revegetation may include topsoil replacement,
planting, seeding, fertilization, liming, and weed-free
mulching as necessary. Use native material where
appropriate and feasible. Use certified weed-free
or weed-seed-free hay or straw where certified materials
are required and/or are reasonably available. Always
use certified materials in areas closed by administrative
order. Where practical, stockpile weed-seed-free
topsoil and replace it on disturbed areas (e.g. road
embankments or landings).
- Use local seeding guidelines to determine detailed
procedures and appropriate mixes. To avoid weed-contamination,
a certified seed laboratory needs to test each lot
against the all-State noxious weed list to Association
of Seed Technologists and Analysts (AOSTA) standards,
and provide documentation of the seed inspection
test. There are plant species not on State and Federal
noxious weed lists that the Forest Service would
consider non-native invasive weeds. Check State and
Federal lists to see if any local weeds need to be
added prior to testing. Seed lots labeled as certified
weed free at time of sale may still contain some
weed seed contamination. Non-certified seed should
first be tested before use.
- Inspect and document all limited term ground-disturbing
operations in noxious weed infested areas for at
least three (3) growing seasons following completion
of the project. For on-going projects, continue to
monitor until reasonable certainty is obtained that
no weeds have occurred. Provide for follow-up treatments
based on inspection results.
- Ditching - Many priority invasive plants
prefer moist soil conditions and are tolerant of saline
environments; therefore they grow very well in highway
drainage ditches and other components of the drainage
system. As the dense root systems of invasive plants
such as purple loosestrife, phragmites and Japanese
knotweed proliferate, they rapidly clog drainage ditches
and reduce sight distances, especially where water
velocities slow, e.g. up gradient of culvert inverts,
above check dams, etc. Due to the rapid growth of
invasive plants, maintenance cycles are far more frequent
where they exist. Prior to excavating the plants from
drainage ditches, the entire invasive plant infestation
should be treated with the appropriate herbicide,
e.g. Rodeo or other aquatic-use registered herbicide.
This will ensure that the plants, seeds and root parts
will not spread and re-establish. Failure to treat
the invasive plants prior to physical removal will
most likely result in immediate re-growth of the plants
in the ditch and the spread of the plant to adjacent
and downstream areas. In addition, if the invasive
plants are not killed prior to ditch cleaning, the
spoil produced can further spread the plants upon
disposal;
- Shoulder Scraping - Removing the build-up
of organic material along highway shoulders is essential
to maintaining pavement quality, providing adequate
sheet flow drainage and providing safe driving conditions.
Due to their disturbed nature and harsh growing conditions,
highway shoulders provide a prime area for invasive
plants to establish and spread. Therefore shoulder
scraping activities address invasive plant control,
though scraping is not a desirable control method
in and of itself. Prior to scraping highway shoulders,
all existing priority invasive plants should be treated
with appropriate herbicide or other control measure
to kill seeds and plant parts, including the root
stock. This will prevent the plant from reseeding,
re-sprouting in-situ or spreading to adjacent areas
via, water, wind, or hitching a ride on equipment
or through spoil disposal.
- Vine, Brush and Tree Removal - Several common
species of vines, brush and trees that grow profusely
along highway roadsides are considered invasive species.
These species frequently cause a nuisance to maintenance
workers, block traffic signs or limit sight distances
and therefore are removed in routine maintenance operations.
In the evaluation of these removal priorities, invasive
species should be given preference and controlled
by accepted practices that will ensure no re-sprouting
and prevent additional spread through seed dispersal.
Since these species do not reproduce vegetatively,
plant parts do not need to be buried or land-filled,
and equipment does not require cleaning. Accepted
methods of control include foliar herbicide treatment
or cutting followed by stump treatment with herbicide.
Mowing alone frequently results in re-sprouting and
cloning and is not an effective control methodology;
- Poisonous Plant Removal - A few invasive
species pose serious a threat to worker safety and
public health. Giant Hogweed, Heraculeum mantegazzianum,
is such a plant. Upon dermal contact this plant causes
severe skin burns which are exacerbated through exposure
to sunlight. Where this plant is encountered, the
location should be located using GPS coordinates and
reference markers identification, the size of the
population should be noted and maintained in a regional
database.
- Disposal – Proper disposal of harvested
invasive plant parts and soil containing invasive
plant seeds or root stock (rhizomes) is essential
to controlling the spread of invasive plants. Full
consideration should be given, as appropriate, as
follows:
- Transportation - While on the treatment
site, bag all cut living plant material in heavy
duty, 3 mil or thicker, black contractor quality
plastic clean-up bags. Securely tie the bags and
transport from the site in a truck with a topper
or cap to securely fasten the load, in order to prevent
spread of the plant material from the project work
site. Transport the material to an appropriate disposal
location.
- Compost - Because of the extremely robust
nature of invasive species, composting in a typical
backyard compost pile or composting bin is not appropriate.
However, methods can be used whereby sun-generated
heat can be used to destroy the harvested plant materials.
For instance, storage in a sealed 3 mil thickness
(minimum) black plastic garbage bags on blacktop
in the sun until the plant materials liquefy is effective.
If a larger section of blacktop is available, make
a black plastic (4 mil thickness minimum) envelope
sealed on the edges with sand bags. The plant material
left exposed to the sun will liquefy in the sealed
envelope without danger of dispersal by wind. The
bags or envelopes must be monitored to make sure
the plants do not escape through rips, tears or seams
in the plastic.
- Bury – Due to the incredible capacity
of many invasive species to reproduce by seed, clone
and vegetative propagation, it is absolutely imperative
that spoil material contaminated with invasive plant
material NOT be disposed-of in an indiscriminant
manner. It is recognized that the Contractor owns
spoil material and therefore, contract documents
should identify locations of contaminated soil and
address disposal options. Spoil material that contains
invasive plant material should be buried in an excavated
pit, covered with woven geotextile and covered with
at least three feet of uncontaminated fill material.
- Landfill – If harvested invasive plant
parts or spoil material containing invasive plant
material is not composted or buried, it should be
transported directly to a sanitary landfill for proper
disposal.
- Bridge Washing – All bridge washing
activities, whether for biannual maintenance or in
preparation for re-painting, require the use of water.
Several invasive plant and animal species are aquatic
or are dispersed through water, therefore, DOT activities
that require the transport and use of water need to
consider invasive species control. Control considerations
include use of municipal water sources, filters on
water intakes, decontamination/sanitation of equipment
and use of in-situ water sources. In addition, the
equipment used in transporting and spraying water
should be cleaned prior to use or between use at sites
in different watersheds.
- Construction Equipment in Water Bodies – Several
invasive species are aquatic and many additional non-aquatic
species are readily spread by the movement of flowing
water. Many aquatic invasive species are capable of
survival out of water for extended periods. To prevent
the accidental introduction of invasive species that
are "hitching a ride" on construction equipment,
all equipment that is to be placed in a water body
should be cleaned, as appropriate, e.g. tracks, buckets,
to remove invasive species and their seeds and propagules.
This requirement applies to equipment arriving on
the project and equipment that is being relocated
within the project;
- Restricted Construction Equipment Access – To
prevent the accidental introduction of invasive plants
during construction or maintenance activities, all
tracked equipment involved in earthwork should be
cleaned to remove plants, seeds and propagules that
may be hitchhiking, prior to arrival on-site. If tracked
equipment is used in earth work on a portion of a
project where invasive species are known to exist,
this portion of the earthwork should be conducted
last, or the equipment shall be cleaned prior to use
on any portion of the site that is known to be free
of invasive plants; and
- Cleaning of Construction Equipment - Cleaning
should occur prior to equipment arriving on-site.
Once on-site, if equipment involved in earthwork is
contaminated with invasive species, the equipment
should be cleaned prior to moving into uncontaminated
areas. Cleaning shall consist of using physical means
and hand tools, such as brushes, brooms, rakes or
shovels, on all track and bucket/blade components
to adequately remove all visible dirt and plant debris.
If water is used, the water/slurry shall be contained
so as to restrict introduction of invasive plants,
seeds and propagules into the project or off-site
through future surplus material disposal.
- Treat weeds at administrative sites and use weed
prevention practices to maintain sites in a weed-free
condition.
- Determine the need for, and when appropriate,
identify sites where equipment can be cleaned. Clean
equipment before entering area targeted for prevention
of invasive, including federal forest and park lands.
When practical, collect and incinerate plant parts.
Remove mud, dirt, and plant parts from project equipment
before moving it into a project area.
- Clean all equipment, before leaving the project
site, if operating in areas infested with weeds.
Determine the need for, and when appropriate, identify
sites where equipment can be cleaned. Seeds and plant
parts need to be collected when practical and incinerated.
- Workers need to inspect, remove, and properly
dispose of weed seed and plant parts found on their
clothing and equipment. Proper disposal means bagging
the seeds and plant parts and incinerating them.
- Set the example; maintain weed- free administrative
sites.
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| 4.10.2
Potential Construction Contract Wording and Measures
for Invasive Species Control |
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The Center for Invasive Plants Management recommends
the following contract language for weed prevention:
[N]
- Prior to any construction disturbance you will:
- Identify and map all noxious and invasive weed
populations present in the project area.
- Treat or contain any weed populations that may
be impacted or disturbed by construction activity.
- Flag all weed populations to be avoided.
- Provide training to construction workers and
equipment operators on the identification of weeds
to be avoided.
- Certify that all construction material sources
used for supplies of sand, gravel, rock and mulch
are weed-free prior to obtaining or transporting
any material from them.Obtain and use only certified
weed-free straw or use fiber roll logs for sediment
containment.
- Wash and inspect all vehicles for weed seeds
and plant parts prior to bringing them onto the
job site.
- Install stormwater Best Management Practices
to prevent erosion of the job site and the potential
transport of weedy material onto or off of the job
site.
- During construction you will:
- Minimize ground disturbance and vegetation removal
as much as possible and practical.
- Wash, or using an air compressor, blow clean
all vehicles (including tires and undercarriage)
that may have entered weed-infested areas prior
to entering uninfested areas of the job site.
- Restrict vehicles or other traffic that may transport
weed seeds or plant material from entering the job
site unless they are first washed and inspected.
- After construction is complete you will:
- Revegetate or otherwise prevent the establishment
of weeds in all areas of the job site through a program
of monitoring and post-construction weed treatment
for the life of the project.
- Revegetate using soil components and mulches obtained
from non-weed infested sources.
- Utilize seed and other plant material that has
been checked and certified as noxious weed-free and
that has a weed content of 0.05 percent or less.
- Revegetate using plant materials that have a high
likelihood of survival.
- Maintain all planted material and native vegetation
located on the project site for the life of the project.
- Monitor all seeded sites for weed infestation.
Treat all weeds adjacent to newly seeded areas prior
to planting and treat planted areas for weeds in
the first growing season.
- NYSDOT utilizes the following contract item methods
of measurement:
- Controlling invasive plants will be measured
as the number of square meters of surface area that
have been satisfactorily controlled. The unit price
bid per square meter shall include the cost of all
labor, materials and equipment, including disposal,
and incidentals necessary to complete the work.
| Item |
Pay Unit |
| Controlling Invasive Plants with Plastic |
Square Meter |
| Controlling Invasive Plants with Herbicides |
Square Meter |
| Controlling Invasive Plants by Pulling |
Square Meter |
| Controlling Invasive Plants by Digging |
Square Meter |
|
| 4.10.3
Review and Pretreatment of Construction and Materials
Sites |
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Pre-construction planning and treatment to
reduce infestations of invasives is on the upswing.
[N]
Nine DOTs (23% of respondents) said that all construction
sites are reviewed for invasive species before opening.
[N]
Wyoming DOT is among five that are working at pretreating
construction zones prior to soil disturbance.
WYDOT is trying to develop a more aggressive pit
assessment and treatment program with local Weed & Pest
districts. These sources have been identified as
having the greatest potential for spreading invasives.
At Nevada DOT a staff biologist surveys material
source sites for invasives. When invasives are found,
a management plan is developed in cooperation with
the local BLM weed coordinator or botanist. Environmental
Services is developing standard noxious weed control
BMP specifications for weed management on material
sites and project sites. Eight other DOTs (23% of
respondents) also ensure dirt and gravel sources
are evaluated.
In addition:
- Over a third of DOTs (17 total) specify weed-free
mulches on all projects. Inert mulch products such
as straw or wood fiber are used in sensitive areas
by 11 DOTs (28% of respondents).
- Twenty-one state DOTs (53% of respondents) specify
on project plans and bid contracts that seed and
sod sources must be free of invasive species and/or
weeds.
Possible solutions to the problem of weeds that
are introduced by animal feed or mulches contaminated
with weed seed are discussed in Certified
Weed Free Forage: An Emerging Program for Western
States, by UC-Davis.
|
| 4.10.4
Protection of Native Populations |
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Intact communities of native species both suppress
invasives and shelter rare species. Thirty-eight
percent (38%) of responding DOTs (15 states) are
now screening for the presence of rare plant communities
in the work zone or ROW. [N]
In 13 states, areas in need of special management
are identified by resource agencies or state Natural
Heritage Program. [N]
North Carolina DOT, like many others, works cooperatively
with their state Department of Environment and Natural
Resources, in-house Botanists, and others to identify
and protect state and federally endangered plant
and animal species found on our rights-of-way. Oregon
DOT has special management areas marked with signs
that indicated the types and timing of maintenance
techniques that are to be performed. Since Wisconsin
DOT (WisDOT) hires County Highway Departments to
perform highway maintenance, WisDOT has let several
contracts to manage/restore high quality remnant
plant communities discovered on the rights-of-way.
Management plans are often developed to inventory
and ensure appropriate management of special areas.
Ten DOTs (25% of respondents) have taken it upon
themselves to map and track protected communities
on the DOT ROW, statewide.
Staff at 14 DOTs (35% of respondents) identify
special management areas, which are managed accordingly
by maintenance forces. [N]
As Illinois DOT described, commitments are added
to plans and DOT staff are trained on how to maintain
these areas through mowing, herbicide applications
and burning. Protected species are identified and
restricted maintenance practices are incorporated
to protect the endangered species; construction
practices are also altered to minimize disturbances
of native plant communities whenever possible (NV).
In several states, from Wisconsin to New York, special
vegetation management programs have been developed
to protect Karner Blue Butterfly habitat, including
mowing date restrictions and native blue lupine
and butterfly weed restoration planting and seeding.
The Louisiana Department of Transportation Development
(LADOTD) has taken high value remnant strips in
several districts and moved them just beyond the
ROW, with the consent of the owners of that property
and discussions regarding proper management. If
moving them is not deemed an option, LADOTD marks
the site to prevent herbicide applications or mowing
at the wrong time of year.
In most cases, DOTs are taking these conservation
measures without knowing the total acreage of high
quality forest, wetland, or native grassland remnants
they have or are protecting in the ROW. Just 15
percent of those responding (6 states) could provide
such an estimate, if asked. More than a third of
DOTs (43% of respondents - 17 states) identify native/rare
plant communities in EAs and EISs. [N]
In fact, Hawaii DOT indicated that most of their
protected areas have been identified as a result
of EAs, EISs, and Special Management Areas.
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| 4.10.5
Vehicle Cleaning Practices |
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Vehicle and equipment cleaning procedures and
practices are typically used to minimize or eliminate
the discharge of pollutants from vehicle and equipment
cleaning operations to storm drain systems or watercourses,
and to minimize transport of invasive species. Twenty-three
percent of responding DOTs (9 DOTs) say they ensure
vehicles are washed before and after use, to control
the spread of invasive species. Caltrans is among
the DOTs that have developed an extensive set of
construction vehicle
cleaning environmental stewardship practices.[N]
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Some DOTs are undertaking research to identify
what vegetation establishment methods work best
in their states and ecoregions. Studies on compost
usage are occurring in the west and mid-west, from
Texas in the south to Idaho in the north. The Nebraska
Department of Roads has research results due soon,
which will be used to develop technical guidelines
for vegetation establishment on roadway shoulders.
The project is examining the interaction effects
of seed priming, type of mulch, and level of irrigation
on soil movement and establishment of the short
grass mixture on the foreslope of roadway shoulders;
and the interaction effects of composted manure
applications and a six to twelve inch compacted
buffer strip between the paved shoulder and the
seedbed on soil movement and establishment of the
short grass mixture on the foreslope of the roadway.
Delaware DOT is also publishing a vegetation management
manual, in conjunction with the agency's tree preservation
policy for a Livable Delaware.[N]
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DOTs are teaching maintenance staff that shoulder
grading is not acceptable as a method of vegetation
or invasive species control. Shoulder grading is
only promoted as a means of refining lateral support
for the road.
|
| 4.10.8
Revegetation and Vegetation Salvage Plan |
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A number of states have developed revegetation
and vegetation salvage plans.Arizona DOT has a policy
for salvage and replanting native trees and shrubs
and plants, with up to $200,000 per mile for major
species.[N]
Revegetation and salvage may occur more easily in more
humid environments with faster re-growth. Recommended
practices for revegetation and vegetation salvage include
the following.
- A revegetation plan should be developed to ensure
that salvage vegetation is used where possible and
that native species are used. Monitoring will occur
during the revegetation period to ensure the success
of the revegetation plan.
- Include at least a one-year plant establishment
guarantee period from the contractor.
- Follow guidelines or specifications for protection/restoration
of existing vegetation. To protect existing desirable
vegetation from construction impacts: [N]
- Identify and delineate in contract documents all
vegetation to be retained and mark in the field prior
to the start of adjacent soil-disturbing activities.
Mark areas to be preserved with orange polypropylene
temporary fencing.
- Minimize disturbed areas by locating temporary
roadways to avoid stands of trees and shrubs and to
follow existing contours to reduce cutting and filling.
- When removing vegetation, consider impacts (increased
exposure or wind damage) to the adjacent vegetation
that will be preserved.
- Protect the root zone of vegetation out to 1.5
times the diameter of the drip line, which is the
outermost reach of its branches (the drip line).
- If cuts or fills are required in the vicinity of
trees to be saved, consider retaining walls, tree
wells, gravel, or drainage systems to protect the
root systems.
- Avoid storing, parking or driving heavy equipment
around the base of a tree, which can compact the soil
and deprive the tree's roots of the water and air
they need to survive. Stockpiling building materials
or fill can have a similar effect. Refer to the Soils
and Soil Amendments section for more information on
soil compaction and its minimization.
- Avoid scraping soil from roots or cutting them
too deeply or too close to the tree can cause the
tree to die or have a weakened hold and blow down.
This damage may not be visible for years .
Mn/DOT has developed a Specification for Protection
and Restoration of Vegetation. This specification promotes
the protection and preservation of vegetation from
damage and the use of corrective action when damage
does occur.[N]
Example
11 : Mn/DOT Specification for Protection and Restoration
of Vegetation Construction Elements
A. Protecting and Preserving
The Contractor shall protect and preserve:
Specimen trees.
- Threatened and endangered plants, as listed on
the federal and state threatened and endangered species
list.
- Vegetation designated in the Contract to be preserved.
- Trees, brush, and natural scenic elements within
the right-of-way and outside the actual limits of
clearing and grubbing.
- Other vegetation the Engineer identifies for protection
and preservation.
The Contractor shall not place temporary structures,
store material, or conduct unnecessary construction
activities within a distance of 25 feet outside of
the dripline of trees designated to be preserved without
approval from the Engineer. The Contractor shall not
place temporary structures or store material (including
common borrow and topsoil ) outside of the construction
limits in areas designated in the Contract to be preserved.
A1 Temporary Fence
The Contractor shall place temporary fences to protect
vegetation before starting construction.
The Contractor shall place temporary fence at the
construction limits and at other locations adjacent
to vegetation designated to be preserved when specified
in the Contract, directed by the Engineer, or allowed
by the Engineer. The Contractor shall not remove the
fence until all work is completed or until removal
is allowed by the Engineer. The fence shall prevent
traffic movement and the placement of temporary facilities,
equipment, stockpiles, and supplies from harming the
vegetation.
A2 Clean Root Cutting
The Contractor shall cleanly cut all tree roots
at the construction limits when specified in the Contract
or directed by the Engineer.
The Contractor shall immediately and cleanly cut
damaged and exposed roots of trees designated for
protection back to sound healthy tissue and shall
immediately place topsoil over the exposed roots.
The Contractor shall limit cutting to a minimum depth
necessary for construction and shall use a vibratory
plow or other approved root cutter prior to excavation.
The Contractor shall immediately cover root ends that
are exposed by excavation activities to within 6 inches
of topsoil as measured outward from root ends.
A8 Destroyed or Disfigured Vegetation
If the Contractor destroys or disfigures vegetation
designated to be preserved, the Contractor shall,
at no expense to the Department, restore the damaged
vegetation to a condition equal to what existed before
the damage was done. The Engineer may assess damages
against the Contractor on vegetation where an equal
level of restoration is not accomplished. The Engineer
will assess damages to trees and landscaping at not
less than the appraisal damages as determined by the
International Society of Arboriculture appraisal guide.
The Engineer will determine and assess damages to
other vegetation.
A10 Other Vegetation Protection Measures
The Contractor shall provide other vegetation protection
measures, including root system bridging, compaction
reduction, aeration, and retaining walls, as specified
in the Contract or as directed by the Engineer.

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An adequately prepared site will have these characteristics:
[N]
- Free of construction debris.
- Relatively few large rocks or other natural objects.
- Free of ruts or gullies.
- Top two inches should be in a friable condition
(non-compacted), ideally allowing a heel to make a ¼-inch
impression.
- Heavily compacted sites should be scarified to
a depth of 6 to 8 inches.
Availability of soil preparation equipment is often
limited, but the Contractor can often use standard
construction machinery. For example, ripper teeth on
a grader tool bar will adequately prepare a site. Ideally,
scarification will be done in two passes perpendicular
to each other. However, on sloping land and in areas
of high wind, use mono-directional scarification perpendicular
to the direction of slope or prevailing wind. If traditional
surface preparation equipment such as disks and/or
chisel plows are available, the conditions required
for adequate surface preparation are the same as previously
noted.
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