HomeMy WebLinkAboutTR_Offsite_Utility_Extension_230807_v2.pdfWASHINGTON 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-
HARMONY RIDGE OFF-SITE UTILITY EXTENSION
15509 116th Avenue SE
Renton, WA 98058
Prepared for: Barghausen Consulting Engineers, Inc.
Prepared by: Washington Forestry Consultants, Inc.
Date of Report: August 7, 2023
Introduction
The project proponent is planning to develop a 0.49-acre utility extension for the Harmony Ridge
project at 15509 116th Avenue SE 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 Tree Protection Ordinance.
•Make recommendations for retention of significant trees, along with required protection
and cultural measures.
Observations
Methodology
WFCI has evaluated all trees 6 inches diameter at breast height (DBH) and larger in the proposed
project area and assessed their potential to be incorporated into the new project. Red alder and
black cottonwood 8 inches and larger DBH were evaluated. 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.
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.
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
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Site Description
The 0.49-acre extension area is located along the SE property line of a parcel owned by the City
of Renton. The site is forested with no improvements in the utility corridor. There is a water tower
facility in the northern portion of the parcel. The topography is flat to gently rolling with a
southerly aspect. There are six single-family home lots to the south of the project area.
Existing Tree Conditions
A total of 78 trees were assessed for the project. The size of significant trees ranges from 6 inches
to 37 inches in diameter at breast height (DBH). Tree species include bigleaf maple (Acer
macrophyllum), black cottonwood (Populus trichocarpa), Douglas-fir (Pseudotsuga menziesii),
red alder (Alnus rubra), western hemlock (Tsuga heterophylla), and western redcedar (Thuja
plicata). Tree conditions on the site range from ‘Dead’ to ‘Very Good’.
Off-site Impacts
Trees outside the limits of construction will be protected by tree protection fencing. Trees whose
health and stability will be compromised by the utility trenching will be removed.
Discussion
Trees Removed for Project
Fifty-seven trees will need to be removed to complete the project. Forty-six of the trees are
healthy, long-term trees and eleven trees are unhealthy.
Tree Density Calculations
Title 4-4-130H of the Renton Municipal Code (RMC) requires 30% of the significant trees to be
retained. There are a total of 57 significant sized trees that require removal for the project. After
allowed tree deductions 46 trees remain for calculating the 30% requirement. A total of 14
significant trees will need to be retained in the project area to meet the requirement.
Total # of Significant Trees: 57 Trees
# of High Risk Significant Trees: 11 Trees
# of Significant Trees After Deductions: 46 Trees
# of Significant Trees Required to be Saved: (46 x 30%) 14 Trees
# of Significant Trees Planned to be Saved 0 Trees
Shortfall of Significant Tree Requirement 14 Trees
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Additionally, RMC 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: 0.49 Acres
Required Tree Credit Density
(0.49 Acres x 30 Credits/Acre): 15.0 Tree Credits
Proposed Tree Retention: (0 trees) 0.0 Tree Credits
Shortfall of Tree Credit Requirement:15.0 Tree Credits
By retaining 0 of the significant trees on the site, this plan falls short of the minimum significant
tree retention requirement by 14 trees. Required tree credit retention falls short of the minimum
tree credits by 15.0 credits. Trees will be required to be replanted to replace the shortfalls. Tree
replacement is necessary because of the unique type of project being proposed, no alternative plans
are available to retain more trees. The trees being removed equates t o 138 replacement credits.
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.
Recommendations
Tree Protection Measures
Off-site edge trees must be protected during construction by a temporary chain-link fence
(Attachment 7), located at the property line. 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 (Table 2). 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.
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
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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.
Pruning and Thinning
Pruning should be done to coincide with land clearing, to facilitate clean-up and while access to
the trees is available.
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. Forty-six healthy trees and 11 unhealthy trees will be removed to complete the utility extension
project.
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 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.
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.
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
Washington Forestry Consultants, Inc. Page 5
Summary
The City of Renton Municipal Code calls for 14 significant trees and 15.0 tree credits to be retained
on the site. Tree replacement is necessary because of the limited alternatives to the project being
proposed. All removal trees will be replaced with plantings. The trees being removed equates to
138 replacement credits that need replacing.
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
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
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Attachment 1. Aerial Photo of Harmony Ridge Off-site Utility Extension Area
(2019 King County iMap)
Approximate Project Area Boundary
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
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Attachment 2. Harmony Ridge Off-site Utility Extension Site Plan
Tree Protection Fence Location
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
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Attachment 3. List of Trees Assessed for Harmony Ridge Off-site Utility
Extension Project
Tree Outside Extension Boundary
Tree # Species DBH
(in.) Condition Dripline
(feet)
Save Based
on
Condition
Alone? Yes
or No
Minimum
Root
Protection
Zone (feet)
Project
Plan -
Save or
Remove
Comment
450002 Western
Redcedar 16 Good 15 Yes 8 Remove
450003 Western
Redcedar 11 Good 15 Yes 6 Remove
450004 Western
Redcedar 19 Good 20 Yes 10 Remove
450001 Bigleaf
Maple 12 Good 20 Yes 6 Save
450005 Bigleaf
Maple
18,
19, 26 Good 30 Yes 19 Save
450006 Bigleaf
Maple 7 Fair 20 Yes 6 Remove
450000 Bigleaf
Maple 7 Good 15 Yes 6 Remove
8 Douglas-fir 22 Good 15 Yes 11 Save no # behind
fence
9 Western
Redcedar 18 Good 17 Yes 9 Save no # behind
fence
10 Western
Hemlock 20 Fair 18 Yes 10 Save no # behind
fence
551912 Bigleaf
Maple 13 Fair 25 Yes 7 Remove
551913 Bigleaf
Maple 12 Good 21 Yes 6 Remove
551914 Bigleaf
Maple 8 Good 25 Yes 6 Remove
551918 Bigleaf
Maple 14, 33 Good 36 Yes 18 Remove
551932 Bigleaf
Maple 15 Good 25 Yes 8 Remove
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Tree # Species DBH
(in.) Condition Dripline
(feet)
Save Based
on
Condition
Alone? Yes
or No
Minimum
Root
Protection
Zone (feet)
Project
Plan -
Save or
Remove
Comment
551933 Bigleaf
Maple 11 Good 30 Yes 6 Remove
800024 Douglas-fir 21 Fair 12 Yes 11 Remove
800025 Bigleaf
Maple 15 Good 20 Yes 8 Remove
800028 Bigleaf
Maple 6 Very Poor 8 No 6 Remove stem decay
800030 Bigleaf
Maple 13, 19 Good 25 Yes 12 Remove 2 stems
800036 Douglas-fir 9 Poor 15 No 6 Remove
Phaeolus
schweinitzii
fruiting body
800037 Bigleaf
Maple 7 Fair 25 Yes 6 Remove leans heavy
to south
800042 Western
Redcedar 17 Good 10 Yes 9 Remove
800043 Western
Redcedar 12 Good 15 Yes 6 Remove
800044 Bigleaf
Maple 24 Good 26 Yes 12 Remove
800046 Bigleaf
Maple 11, 15 Good 25 Yes 10 Save
800047 Bigleaf
Maple 21 Good 30 Yes 11 Remove
800053 Bigleaf
Maple 11, 12 Good 20 Yes 8 Remove
800054 Bigleaf
Maple 11 Good 20 Yes 6 Remove
800935 Black
Cottonwood 32 Poor 20 No 16 Remove hollow butt
800947 Red Alder 11, 13 Very Poor 10 No 9 Remove dead tops, in
decline
800948 Red Alder 14 Dead 0 No 7 Remove
800949 Cascara 5 Fair 4 Yes 6 Remove
800950 Bigleaf
Maple 6 Fair 8 Yes 6 Remove
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
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Tree # Species DBH
(in.) Condition Dripline
(feet)
Save Based
on
Condition
Alone? Yes
or No
Minimum
Root
Protection
Zone (feet)
Project
Plan -
Save or
Remove
Comment
800951 Red Alder 8 Very Poor 10 No 6 Remove dead tops
800952 Red Alder 8 Dead 0 No 6 Remove
800953 Red Alder 10 Very Poor 10 No 6 Remove dead tops
800956 Douglas-fir 17 Fair 18 Yes 9 Remove
800957 Red Alder 16 Very Poor 15 No 8 Remove dead tops
800958 Western
Redcedar 16 Very Good 15 Yes 8 Save
800961 Red Alder 14 Dead 0 No 7 Remove
800972 Douglas-fir 27 Good 30 Yes 14 Remove
800973 Douglas-fir 37 Good 35 Yes 19 Remove
800976 Douglas-fir 20 Good 20 Yes 10 Remove
800977 Bigleaf
Maple 13 Good 25 Yes 7 Save
800981 Bigleaf
Maple 7 Good 10 Yes 6 Remove
800982 Bigleaf
Maple 12 Good 24 Yes 6 Remove
800984 Bigleaf
Maple 8, 9 Good 26 Yes 6 Save
800985 Bigleaf
Maple 9 Good 25 Yes 6 Remove
800995 Bigleaf
Maple 9 Good 15 Yes 6 Save
800996 Western
Redcedar 9 Good 10 Yes 6 Remove
800997 Douglas-fir 29 Fair 25 Yes 15 Remove
800999 Western
Redcedar 22 Good 15 Yes 11 Remove
801000 Western
Redcedar 7 Good 10 Yes 6 Remove
801002 Bigleaf
Maple 11, 14 Good 26 Yes 9 Remove
801004 Bigleaf
Maple 35 Fair 40 Yes 18 Remove
801005 Douglas-fir 13 Poor 15 No 7 Remove stem wound
801006 Douglas-fir 7 Fair 12 Yes 6 Remove
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Tree # Species DBH
(in.) Condition Dripline
(feet)
Save Based
on
Condition
Alone? Yes
or No
Minimum
Root
Protection
Zone (feet)
Project
Plan -
Save or
Remove
Comment
801007 Bigleaf
Maple 10, 17 Good 30 Yes 10 Remove
801008 Douglas-fir 24 Good 17 Yes 12 Remove
801013 Bigleaf
Maple 10 Good 20 Yes 6 Save
801014 Western
Redcedar 25 Good 20 Yes 13 Save
801016 Bigleaf
Maple 8 Good 15 Yes 6 Remove
801017 Douglas-fir 27 Good 16 Yes 14 Remove
801033 Douglas-fir 15 Good 19 Yes 8 Save
801036 Douglas-fir 22 Fair 20 Yes 11 Save
801037 Douglas-fir 35 Very Good 30 Yes 18 Save
801039 Bigleaf
Maple 11 Fair 15 Yes 6 Remove
801042 Western
Redcedar 15 Good 15 Yes 8 Remove
801043 Western
Redcedar 11 Good 15 Yes 6 Remove
801044 Bigleaf
Maple
15,
22, 22 Good 30 Yes 18 Remove
801045 Western
Redcedar 9 Good 10 Yes 6 Remove
801046 Bigleaf
Maple 11 Good 22 Yes 6 Save
801048 Douglas-fir 33 Good 25 Yes 17 Save
801053 Bigleaf
Maple 6 Good 15 Yes 6 Save
801054 Western
Redcedar 10 Good 10 Yes 6 Save
801056 Western
Redcedar 7 Good 12 Yes 6 Save
801057 Western
Redcedar 6 Good 10 Yes 6 Save
801066 Western
Redcedar 14 Very Good 15 Yes 7 Save
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Washington Forestry Consultants, Inc. Page 12
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
• No or minor insect or disease problems
• Mortality expected within the next few years
Dead DEAD • Dead
Harmony Ridge Off-site Utility Extension –Tree Protection Plan
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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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Washington Forestry Consultants, Inc. Page 17
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 Forestry 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.