HomeMy WebLinkAboutEX_03_RS_Preliminary_Tree_Protection_Plan_230825_v1 WASHINGTON FORESTRY CONSULTANTS, INC.
FORESTRY AND VEGETATION MANAGEMENT SPECIALISTS W F C I
O: 360/943-1723 C: 360/561-4407
9136 Yelm Hwy SE
Olympia, WA 98513
URBAN/RURAL FORESTRY • TREE APPRAISAL • TREE RISK ASSESSMENT
RIGHT-OF-WAYS • VEGETATION MANAGEMENT • FOREST/TREE MGT. PLANS • EXPERT TESTIMONY
Member of International Society of Arboriculture and Society of American Foresters
- Preliminary Tree Protection Plan-
TALBOT ROAD PROJECT
2103 Talbot Road South
Renton, WA 98055
Prepared for: Lili Lu / 吕莉莉
CEO
Global Land LLC
Prepared by: Washington Forestry Consultants, Inc.
Date of Report: June 26, 2023
Introduction
The project proponent is planning to construct a new 6-lot short plat on one parcel totaling 1.39-
acres at 2103 Talbot Road South in Renton. The proponent has retained WFCI to:
• Evaluate and inventory all trees on the site pursuant to the requirements of the City of
Renton 4-4-130 Tree Retention and Land Clearing Regulations.
• Make recommendations for retention of significant trees, along with required protection
and cultural measures.
Observations
Methodology
WFCI has evaluated all trees with a caliper of at least 6" diameter at breast height (DBH), except
alder or cottonwood trees, which qualify as significant trees with a caliper of 8" or greater. To be
a significant tree, it must have a condition rating of Fair or better. Trees rated as Poor, Very
Poor, or Dead or are defective, diseased and/or in decline and are not long-term trees and are not
considered to be significant trees. All off-site trees with driplines or root protection zones
(RPZ’s) encroaching the site were assessed as well.
RECEIVED
09/08/2023 JDing
PLANNING DIVISION
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The tree evaluation phase used methodology developed by Nelda Matheny and Dr. James Clark
in their 1998 publication Trees and Development: A Technical Guide to Preservation of Trees
during Land Development.
Site Description
The project site consists of one 1.39-acre parcel, # 7222000175. The cover type on the site is
dominated by a grass pasture area in the southern half of the parcel. A single-family home and
associated outbuildings are in the northern half. The topography moderately slopes to the west
from the house area. The site has a westerly aspect. There are high voltage transmission
powerlines that run along the west property line. The project is bordered by single-family homes
to the north and south, Talbot Road S. to the east, and Shattuck Avenue S. to the west.
Soils Description
According to the USDA Natural Resource Conservation Service soil survey the soil type in the
project area is the Beausite gravelly sandy loam, a moderately deep, well-drained soil. It is
formed as glacial till over residuum from sandstone. Permeability is moderately high to high.
Available water capacity is low. Lithic bedrock occurs at a depth of 24 to 40 inches. The
effective rooting depth for trees is to the bedrock. The potential for windthrow of trees is slight
under normal conditions. New trees require irrigation for establishment.
Figure 1. Talbot Road Project Soils Map
BeC – Beausite gravelly sandy loam
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Existing Tree Conditions
There is one forest cover type on the project area for the purpose of description. The aerial photo
of the project, with tree locations, is shown in Attachment 1.
Type I. -- This cover type covers the entire project site. There are a total of 26 trees in the type.
There are introduced trees planted around the home and naturally seeded native trees growing on
the perimeters of the site. The size of significant trees ranges from 6 inches to 30 inches in
diameter at breast height (DBH). Tree species include apple (Malus spp.), bigleaf maple (Acer
macrophyllum), cherry (Prunus spp.), cypress (Cupressus spp.), flowering dogwood (Cornus
florida), hawthorn (Crataegus monogyna), English holly (Ilex aquifolium), and Oregon ash
(Fraxinus latifolia).
Tree conditions on the site range from ‘Very Poor’ to ‘Good,’ with just over half the trees (54%)
described as being in ‘Poor’ or worse condition. The high number of trees in poor condition is
due to trees under the overhead powerlines that have been topped multiple times for clearance.
The topping has created areas of decay in the tree’s upper canopies. The trees should be
removed and the area re-planted with a small scale tree that will not need continual clearance
pruning.
Table 1. Summary of trees on Talbot Road Project Site.
Species
DBH
Range
(in.)
Condition Range
Total #
of Trees
# of
Healthy
Trees
# of
Unhealthy
Trees*
Species
Composition
of the Stand
Apple 6 – 21 Very Poor - Good 6 4 2 23
Bigleaf
Maple 15 – 25 Very Poor – Poor 3 0 3 12
Cherry 6 – 17 Poor – Good 4 1 3 15
Cypress 19 – 20 Good 2 2 0 8
Flowering
Dogwood 8 Good 1 1 0 3
Hawthorn 6 – 14 Good 3 3 0 12
Holly 7 – 18 Poor – Good 2 1 1 8
Oregon Ash 6 – 30 Very Poor – Poor 5 0 5 19
Sum 6 - 30 Very Poor - Good 26 12 14 100%
*Trees rated as dead, very poor, or poor.
Twelve of the 26 significant trees could be potentially retained on this site when only tree health
is considered. The remaining trees are in poor health or have been topped. One holly tree that
has some top dieback but will be saved as part of the project.
There are 3 Landmark sized trees on the project site. Only one of those trees is healthy and
would make good long-term trees to save. The one healthy Landmark tree is proposed to be
retained.
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The understory vegetation throughout the type is grass, weeds, and other planted shrubs in the
landscape.
Photo 1: View of trees 1 – 9 on the Talbot Road Project Site.
Off-site Impacts
There are no off-site trees that will be impacted from grading on the project. A few small
landscape trees have branches that overhang the site. The branches can be pruned back to the
property line without causing damage to the trees.
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Discussion
Potential for Tree Retention
There are four trees that have the potential to be retained with this site plan. All the trees are
located on lot 6 around the existing home that will be saved as part of the project. The one
healthy Landmark tree is being saved. The remaining trees are all under the footprints of
improvements.
Tree Density Calculations
Title 4-4-130H(a) of the Renton Municipal Code (RMC) requires 30% of the significant trees on
the site to be retained. There are a total of 26 significant sized trees on the parcel. After allowed
tree deductions 16 trees remain for calculating the 30% requirement. A total of 5 significant
trees will need to be retained in the project area to meet the requirement.
Total # of Significant Trees: 26 Trees
# of High Risk Significant Trees: 0 Trees
# of Trees in the Public Rights-of-Ways: 10 Trees
# of Significant Trees After Deductions: 16 Trees
# of Significant Trees Required to be Saved
(30% of 16 Trees): 5 Trees
# of Significant Trees Planned to be Saved 4 Trees
Shortfall of Significant Tree Requirement 1 Tree
Additionally, RMC4-4-130H(b) requires a minimum tree credit density of 30 tree credits per acre
of net developable acreage. The following is a summary of the projected tree density
requirements:
Gross Site Acreage: 1.39 Acres
Designated Public Rights-of-way: 0.0 Acres
Net Developable Acres: 1.39 Acres
Required Tree Credit Density
(1.39 Acres x 30 Credits/Acre): 42.0 Tree Credits
Proposed Tree Retention:
Developed Area (4 trees) 32.0 Tree Credits
Shortfall of Tree Credit Requirement: 10.0 Tree Credits
By retaining 4 of the significant trees on the site, this plan falls short of the minimum significant
tree retention requirement by 1 tree. Required tree credit retention is less than the minimum tree
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credits by 10.0 credits. Additional trees will be required to be replanted to replace minimum
shortfall. When the required number of protected trees cannot be retained, replacement trees,
with at least a two-inch (2") caliper deciduous or an evergreen at least six feet (6') tall, shall be
planted based on the tree credit value of each protected tree removed. A fee in lieu of tree
planting, the cost of which can be determined by the City of Renton can also substitute for tree
replacement if replanting on-site is not feasible.
All reasonable efforts have been taken to preserve trees utilizing the highest priority possible.
The retention of higher priority trees is not feasible or practical for the project site due to the
required improvements along Shattuck Avenue. The trees in this area that form a continuous
canopy are in poor condition from topping. The location of trees and the lot layout limits the
number of trees that can be retained on this project.
Recommendations
Tree Protection Measures
All save trees, including off-site edge trees, must be protected during construction by a
temporary chain-link fence (Attachment 7). Placards shall be placed on the fencing every 50 feet
indicating the words, "NO TRESPASSING - Protected Trees". The individual tree RPZ is the
dripline (6 feet minimum), unless otherwise delineated by WFCI in the field and described in the
attached tree list (Attachment 3). If approved, the silt-fence could double as the tree protection
fence for select off-site trees.
Tree protection fences should be placed around the edge of the root protection zone (RPZ). The
fence should be erected after logging but prior to the start of clearing. The fences should be
maintained until the start of the landscape installation.
There should be no equipment activity (including rototilling) within the root protection zone. No
irrigation lines, trenches, or other utilities should be installed within the RPZ. Cuts or fills
should impact no more than 20% of a tree’s root system. If topsoil is added to the root zone of a
protected tree, the depth should not exceed 2 inches of a sandy loam or loamy fine sand topsoil
and should not cover more than 20% of the root system.
If roots are encountered outside the RPZ during construction, they should be cut cleanly with a
saw and covered immediately with moist soil. Noxious vegetation within the root protection
zone should be removed by hand. If a proposed save tree must be impacted by grading or fills
more than allowed for by WFCI in the tree list, then the tree should be re-evaluated by WFCI to
determine if the tree can be saved with mitigating measures, or if the tree should be removed.
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Pruning and Thinning
Pruning should be done to coincide with land clearing, to facilitate clean-up and while access to
the trees is available (before houses are constructed).
All individual trees to be saved near or within developed areas should have their crowns raised to
provide a minimum of 8 feet of ground clearance over sidewalks and landscape areas, 15 feet
over parking lots or streets, and at least 10 feet of building clearance. Care will need to be taken
to avoid trespassing when pruning offsite trees. This is best achieved by getting cooperation and
permission from the tree owner. If no permission is obtained, then legally one cannot prune
beyond the property line – ground to sky.
All pruning should be done according to the ANSI A300 standards for proper pruning and be
completed by an International Society of Arboriculture Certified Arborist®, or be supervised by a
Certified Arborist®.
Conclusions and Timeline for Activity
1. Four significant trees equaling 32.0 tree credits are proposed to be retained on the site.
2. The final, approved tree protection plan map should be included in the construction drawings
for bid and construction of the project and should be labeled as such.
3. Stake and heavily flag the clearing limits.
4. Contact WFCI to attend pre-job conference and discuss tree protection issues with
contractors. WFCI can verify all trees to be saved and/or removed are adequately marked.
5. Conduct logging. Complete necessary hazard tree removals and invasive plant removals
from the tree protection areas. No equipment should enter the tree protection areas during
logging.
6. Before land clearing is complete, do all necessary pruning on save trees and off-site trees to
provided new home clearances.
7. Contact WFCI to inspect the tree tracts after logging, but prior to land clearing to identify
any additional hazard trees that should be removed.
8. Install tree protection fences along the 'limits of construction'. The fences should be located
at the limits of construction or at the dripline of the save tree or as otherwise specified by
WFCI. Maintain fences throughout construction.
9. Complete clearing of the project.
10. Do not excavate stumps within 10’ of trees to be saved. These should be individually
evaluated by WFCI to determine the method of removal.
11. Complete grading and construction of the project.
12. Contact WFCI to final inspect the tree protection areas after grading.
13. All save trees within reach of targets should be inspected annually for 2 years by a qualified
professional forester retained by the homeowner’s association, and bi-annually thereafter.
The purpose of these inspections is to identify trees that develop problems due to changing
micro-site conditions and to prescribe cultural care or removal.
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Summary
The City of Renton Municipal Code calls for 5 of the healthy, significant trees and 42.0 tree
credits to be retained on the site. Based on the current site plan, 4 existing trees equaling 32.0
tree credits will be retained. One additional tree will be required to replace the 30% significant
tree requirement shortfall. In addition, ten tree credits will need to be replaced.
Please give us a call if you have any questions.
Respectfully submitted,
Washington Forestry Consultants, Inc.
Galen M. Wright, ACF, ASCA Joshua Sharpes
ISA Bd. Certified Master Arborist PN-129BU Professional Forester
Certified Forester No. 44 ISA Certified Arborist®,
ISA Tree Risk Assessor Qualified Municipal Specialist, PN- 5939AM
ASCA Tree and Plant Appraisal Qualified ISA Tree Risk Assessor Qualified
attachments: 1: aerial photo of project area
2: site plan
3: tree list
4: individual tree rating key
5: description of tree evaluation methodology
6: glossary of terms
7: tree protection fence detail
8: assumptions and limiting conditions
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Attachment 1. Aerial Photo of Talbot Road Project
(2019 King County)
Project Area Boundary
Healthy Tree
Unhealthy Tree
1 2 3
4
9
10 11 12 13
14
15
16 17 18 19
20
26
25
24
23 22 21
8 7 6 5
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Attachment 2. Talbot Road Project Site Plan
Project Area Boundary
Retained Tree
Tree Protection Fence Locations
1
2 3
4 Existing
house to
remain
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Attachment 3. List of Trees on Talbot Road Project Tree # Species DBH (in.) Calculated DBH (in.) Condition Average Dripline (feet) Landmark Tree Save Based on Condition Alone? Yes or No Minimum Root Protection Zone (feet) Project Plan. Save or Remove Tree Credits Comment 1 Cypress 20 20 Good 10 Yes 10 Save 8
2 Cypress 19 19 Good 8 Yes 10 Save 8
3 Holly 17,
18 25 Good 8 X Yes 13 Save 10
4 Holly 7, 8,
10 15 Poor 8 No 8 Save 6 dying top
5 Apple 6, 8 10 Good 10 Yes 5 Remove 5
6 Apple 6 6 Good 7 Yes 3 Remove 4
7 Apple 19 19 Good 13 Yes 10 Remove 8
8 Apple 21 21 Good 15 Yes 11 Remove 8
9 Flowering
Dogwood 8 8 Good 10 Yes 6 Remove 4
10 Bigleaf
Maple 15 15 Very
Poor 19 No 8 Remove 6 5 sprouts off old stump
11 Hawthorn 14 14 Good 12 Yes 7 Remove 6
12 Apple 10 10 Very
Poor 10 No 6 Remove 5 dead top, poor tree
13 Hawthorn 14 14 Good 14 Yes 7 Remove 6
14 Cherry 5, 5 7 Good 20 Yes 4 Remove 4
15 Oregon
Ash 6, 10 12 Very
Poor 20 No 6 Remove 5 dead tops, mostly dead
16 Hawthorn 6 6 Good 15 Yes 6 Remove 4
17 Bigleaf
Maple 22 22 Poor 20 No 11 Remove 9 topped multiple times for
powerlines
18 Bigleaf
Maple
18,
18 25 Poor 20 No 13 Remove 10 topped multiple times for
powerlines
19 Apple 20 20 Poor 19 No 10 Remove 8 topped multiple times for
powerlines
20 Cherry 6, 7 9 Poor 14 No 6 Remove 4 topped multiple times for
powerlines
21 Cherry 6-12 17 Poor 18 No 9 Remove 7 4 stems, topped multiple
times for powerlines
22 Oregon
Ash 30 30 Poor 23 X No 15 Remove 11 topped multiple times for
powerlines
23 Oregon
Ash
13,
14 19 Poor 15 No 10 Remove 8 topped multiple times for
powerlines
24 Cherry 14 14 Poor 18 No 7 Remove 6 topped multiple times for
powerlines
25 Oregon
Ash 24 24 Poor 17 X No 12 Remove 9 topped multiple times for
powerlines
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Tree # Species DBH (in.) Calculated DBH (in.) Condition Average Dripline (feet) Landmark Tree Save Based on Condition Alone? Yes or No Minimum Root Protection Zone (feet) Project Plan. Save or Remove Tree Credits Comment 26 Oregon
Ash 22 22 Poor 18 No 11 Remove 9 topped multiple times for
powerlines
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Attachment 4. Individual Tree Rating Key for Tree Condition
RATING SYMBOL DEFINITION
Very Good VG • Balanced crown that is characteristic of the species
• Normal lateral and terminal branch growth rates for the species and
soil type
• Stem sound, normal bark vigor
• No root problems
• No insect or disease problems
• Long-term, attractive tree
Good G • Crown lacking symmetry but nearly balanced
• Normal lateral and terminal branch growth rates for the species and
soil type
• Minor twig dieback O.K.
• Stem sound, normal bark vigor
• No root problems
• No or minor insect or disease problems – insignificant
• Long-term tree
Fair F • Crown lacking symmetry due to branch loss
• Slow lateral and terminal branch growth rates for the species and
soil type
• Minor and major twig dieback – starting to decline
• Stem partly unsound, slow diameter growth and low bark vigor
• Minor root problems
• Minor insect or disease problems
• Short-term tree 10-30 years
RATING SYMBOL DEFINITION
Poor P • Major branch loss – unsymmetrical crown
• Greatly reduced growth
• Several structurally import dead or branch scaffold branches
• Stem has bark loss and significant decay with poor bark vigor
• Root damage
• Insect or disease problems – remedy required
• Short-term tree 1-10 years
Very Poor VP • Lacking adequate live crown for survival and growth
• Severe decline
• Minor and major twig dieback
• Stem unsound, bark sloughing, previous stem or large branch
failures, very poor bark vigor
• Severe root problems or disease
• Major insect or disease problems
• Mortality expected within the next few years
Dead DEAD • Dead
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Cultural Care Needs:
ABBRV. ACTIVITY DESCRIPTION
CC Crown
Cleaning
Pruning of dead, dying, diseased, damaged, or defective branches over 1/2 inch in
diameter –includes removal of dead tops
CT Crown
Thinning
Pruning of branches described in crown cleaning, plus thinning of up to 20% of the live
branches over ½ inch diameter. Branch should be 1/3 to ½ the diameter of the lateral
branch. Thinning should be well distributed throughout crown of tree, and should
release healthy, long-term branches.
RC Crown
Reduction
Reduction of the crown of a tree by pruning to lateral branches. Generally used to
remove declining branches or to lighten end weight on long branches.
CR Crown
Raising
Pruning of lower branches to remove deadwood or to provide ground or building
clearances.
RMV Remove Remove tree due to decline or hazardous conditions that cannot be mitigated by
pruning.
RS Remove
Sprouts
Remove basal sprouts from stem of tree.
Rep Replace Tree is small – is in decline or dead. Replace with suitable tree species.
HT Hazard Tree Tree is hazardous and cannot be mitigated by pruning. Recommendation is to remove
tree.
None No Work No work necessary at this time.
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Attachment 5. Description of Tree Evaluation Methodology
The evaluation of the tree condition on this site included the visual assessment of:
1. Live-crown ratio,
2. Lateral and terminal branch growth rates,
3. Presence of dieback in minor and major scaffold branches and twigs,
4. Foliage color,
5. Stem soundness and other structural defects,
6. Visual root collar examination,
7. Presence of insect or disease problems.
8. Windfirmness if tree removal will expose this tree to failure.
In cases where signs of internal defect or disease were suspected, a core sample was taken to
look for stain, decay, and diameter growth rates. Also, root collars were exposed to look for the
presence of root disease.
In all cases, the overall appearance of the tree was considered relative to its ability to add value
to either an individual lot or the entire subdivision. Also, the scale of the tree and its proximity
to both proposed and existing houses was considered.
Lastly, the potential for incorporation into the project design is evaluated, as well as potential site
plan modifications that may allow otherwise removed tree(s) to be both saved and protected in
the development.
Trees that are preserved in a development must be carefully selected to make sure that they can
survive construction impacts, adapt to a new environment, and perform well in the landscape.
Healthy, vigorous trees are better able to tolerate impacts such as root injury, changes in soils
moisture regimes, and soil compaction than are low vigor trees.
Structural characteristics are also important in assessing suitability. Trees with significant decay
and other structural defects that cannot be treated are likely to fail. Such trees should not be
preserved in areas where damage to people or property could occur.
Trees that have developed in a forest stand are adapted to the close, dense conditions found in
such stands. When surrounding trees are removed during clearing and grading, the remaining
trees are exposed to extremes in wind, temperature, solar radiation, which causes sunscald, and
other influences. Young, vigorous trees with well-developed crowns are best able to adapt to
these changing site conditions.
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Attachment 6. Glossary of Forestry and Arboricultural Terminology
DBH: Diameter at Breast Height (measured 4.5 ft. above the ground line on the high side of the
tree).
Live Crown Ratio: Ratio of live foliage on the stem of the tree. Example: A 100’ tall tree with
40 feet of live crown would have a 40% live crown ratio. Conifers with less than 30%
live crown ratio are generally not considered to be long-term trees in forestry.
Crown: Portion of a trees stem covered by live foliage.
Crown Position: Position of the crown with respect to other trees in the stand.
Dominant Crown Position: Receives light from above and from the sides.
Codominant Crown Position: Receives light from above and some from the sides.
Intermediate Crown Position: Receives little light from above and none from the sides. Trees
tend to be slender with poor live crown ratios.
Suppressed Crown Position: Receives no light from above and none from the sides. Trees
tend to be slender with poor live crown ratios.
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Attachment 7. Tree Protection Fence Detail
6 ft. Temporary Chain Link Fence
NO TRESPASSING - Protected Trees
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Attachment 8. Assumptions and Limiting Conditions
1) Any legal description provided to the Washington Forestry Consultants, Inc. is assumed to be correct. Any
titles and ownership's to any property are assumed to be good and marketable. No responsibility is assumed
for matters legal in character. Any and all property is appraised or evaluated as though free and clear, under
responsible ownership and competent management.
2) It is assumed that any property is not in violation of any applicable codes, ordinances, statutes, or other
governmental regulations, unless otherwise stated.
3) Care has been taken to obtain all information from reliable sources. All data has been verified insofar as
possible; however, Washington Forestry Consultants, Inc. can neither guarantee nor be responsible for the
accuracy of information.
4) Washington Forestry Consultants, Inc. shall not be required to give testimony or to attend court by reason of
this report unless subsequent contractual arrangements are made, including payment of an additional fee for
such services as described in the fee schedule and contract of engagement.
5) Loss or alteration of any part of this report invalidated the entire report.
6) Possession of this report or a copy thereof does not imply right of publication or use for any purpose by any
other than the person to whom it is addressed, without the prior expressed written or verbal consent of
Washington Forestry Consultants, Inc.
7) Neither all or any part of the contents of this report, nor copy thereof, shall be conveyed by anyone, including
the client, to the public through advertising, public relations, news, sales or other media, without the prior
expressed written or verbal consent of Washington Forestry Consultants, Inc. -- particularly as to value
conclusions, identity of Washington Forestr y Consultants, Inc., or any reference to any professional society or
to any initialed designation conferred upon Washington Forestry Consultants, Inc. as stated in its
qualifications.
8) This report and any values expressed herein represent the opinion of Washington Forestry Consultants, Inc.,
and the fee is in no way contingent upon the reporting of a specified value, a stipulated result, the occurrence
neither of a subsequent event, nor upon any finding in to reported.
9) Sketches, diagrams, graphs, and photographs in this report, being intended as visual aids, are not necessarily
to scale and should not be construed as engineering or architectural reports or surveys.
10) Unless expressed otherwise: 1) information contained in this report covers only those items that were
examined and reflects the condition of those items at the time of inspection; and 2) the inspection is limited to
visual examination of accessible items without dissection, excavation, probing, or coring. There is no
warranty or guarantee, expressed or implied, that problems or deficiencies of the tree or other plant or
property in question may not arise in the future.
Note: Even healthy trees can fail under normal or storm conditions. The only way to eliminate all risk is to remove
all trees within reach of all targets. Annual inspections by an ISA Certified Arborist or Certified Forester will
reduce the potential of tree failures. It is impossible to predict with certainty that a tree will stand or fail, or the
timing of the failure. It is considered an ‘Act of God’ when a tree fails, unless it is directly felled or pushed over by
man’s actions.
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