HomeMy WebLinkAboutTR_Arborist_ Report_170920_v1FORESTRY AND VEGETATION MANAGEMENT SPECIALISTS
WFCI
3601943-1 723
FAX 3601943-4 1 28
1919 Yelm Hwy SE, Suite C
Olympia, WA 98501
URBANIRURAL FORESTRY TREE APPRAISAL HAZARD TREE ANALYSIS
RIGHT-OF-WAYS VEGETATION MANAGEMENT ENVIRONMENTAL STUDIES CONTRACT FORESTERS
Member of International Society of Arboriculture and Society of American Foresters
- Final Tree Protection Plan -
VUECREST
4909 Main Ave South
Renton, WA
Prepared for: KBS III, LLC.
Prepared by: Washington Forestry Consultants, Inc.
Date: January 13, 2015
Introduction
The project proponent is planning to construct a new 7 lot subdivision on ~2.42 acres at 4909
Main Ave South in Renton, WA. 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 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. All trees were
numbered at their base. The trees in the northwest corner of the property, a wetland and
associated buffer area, were not individually evaluated. Additionally, red alder (Alnus rubra),
black cottonwood (Populus trichocarpa), and Scouler's willow (Salix scouleriana) trees are not
included in this evaluation as per Renton Code.
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.
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Site Description
The site has an existing home, with a garage and a small shed. The forest was logged many years
ago leaving a sparse stand of residual trees. The site was not replanted and bigleaf maple
resprouts, red alder, and willow grew back and dominate the site today. A small number of
planted trees occur. Overall, tree quality is very poor. The trees on site range between
approximately 10 and 70 years old. The site is relatively flat, with the exception of the northwest
corner where the topography slops down toward a small wetland.
Soil Description
According to the USDA Web Soil Survey the soil type is the Alderwood gravelly sandy loam
(AgC), a moderately deep, moderately well drained soil found on glacial till plains. It is formed
in ablation till overlying basal till. A weakly cemented hardpan is at a depth of 20 to 40 inches.
Permeability is moderately rapid above the hardpan and very slow in the pan. Available water
capacity is low. The effective rooting depth for trees is 20-40 inches. A perched seasonal high
water table is at a depth of 18-36 inches from November to March. The potential for windthrow
of trees is moderate under normal conditions. New trees require irrigation for establishment.
In areas where grading brings the hardpan nearer to the surface, the hardpan must be
fractured under new trees to provide soil volume for root development and to improve
drainage around the tree.
Figure 1. Soils map from NRCS showing 1 soil type – Alderwood gravelly sandy loam.
Tree Conditions
The project area consists of one forest cover type, ~90% of which is a natural stand. An
inventory and assessment of the trees in the stand was conducted to determine the composition
and health of the forest.
Type I. -- Most of the trees in this type are native species. The native species found in this type
include bigleaf maple (Acer macrophyllum), Douglas-fir (Pseudotsuga menziesii), western red
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cedar (Thuja plicata), western hemlock (Tsuga heterophylla), and western white pine (Pinus
monticola). Other less prevalent tree species scattered across the type include apple cultivars
(Malus domestica), black locust (Robinia pseudoacacia), cherry (Prunus spp.), crabapple (Malus
spp.), American holly (Ilex opaca), lodgepole pine (Pinus contorta), and Norway spruce (Picea
abies).
A total of 117 trees exist on the parcel, ranging in diameter from 3 to 38 inches DBH. Sixty-
eight (68) of the trees were classified as sound, healthy, long-term trees in the dominant and co-
dominant crown class. The other 49 trees are not long-term trees due to structural defects or
poor health (dead, diseased, or hazardous).
Table 1. Summary of Trees in Type I.
Species
DBH
Range (in.) Trees/acre
Total # of
Trees
# of
Healthy
Trees
# of
Trees in
Poor
Health*
Species
Composition
of Stand
Bigleaf Maple 4-26 24.7 60 31 29 51.3%
Douglas-fir 7-38 14.7 32 27 5 27.3%
Western Red
Cedar
6-18 2.8
6 5 1 5.1%
Western
Hemlock
6-22 0.9
2 1 1 1.7%
Western
White Pine
13-22 1.8 4 3 1 3.4%
Other** 3-24 6.9 13 1 12 11.1%
Sum 3-38 53.9 117 68 49 100%
*Dead, diseased, or hazardous.
**Less prevalent tree species.
Off-Site Impacts
Tree removal on this parcel will not impact trees on any surrounding parcels.
Discussion
Potential for Tree Retention
The only potential for retaining existing trees in this project is along the southerly parcel
boundary at the back lots 1, 5, and 6, and in the open space in the southwest corner of the parcel.
Eleven trees occur that are suitable for retention in these areas. The proposed ‘save’ trees are
illustrated on the proposed site plan in Attachment #2. A detailed list of all trees by species,
DBH, crown position, condition, root protection zone (RPZ), drip line (D/L) radius, save/remove
potential, and retention availability is provided in Attachment #3.
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Tree Density Calculations
Title 4-4-130 of the Renton Municipal Code requires that a minimum of 30% of all healthy
significant trees in buildable areas be retained on the project. The following is a summary of the
required and planned tree retention:
Total Project Area 2.45 acres
Critical Areas and Buffers 0.19 acres
Rights-of-ways 0.58 acres
Buildable Area 1.68 acres
Total Number of Significant Trees on Site (excluding critical areas) 117 trees
Trees Excluded from Retention Calculation:
Trees that are Dead Diseased or Dangerous 49 trees
Healthy Trees in Proposed Public Streets 30 trees
Trees in Critical Areas and Buffers (Not Inventoried) N/A
Number of Healthy, Significant Trees in Buildable Area: 38 trees
Required Tree Retention:
30% of healthy significant trees in buildable area: 11 trees
Planned Tree Retention 11 trees
Excess of Retention over the Minimum Requirement 0 trees
There are 38 healthy significant trees in the buildable area of the site. At least 11 of these trees
need to be retained to meet the 30% requirement of the City of Renton Code. The proposed plan
retains 11 trees outside of the critical areas and buffers, which meets the minimum retention
requirement. No tree replacement will be required.
The landscape plan (prepared by others) should incorporate some native conifer trees along with
deciduous accent and shade trees to provide a mix of color, texture, and size in the project.
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Recommendations
Tree Protection Measures
Trees to be saved must be protected during construction by a six foot high chain link fencing
(Attachment #8), located at the edge of the critical root zone (CRZ). Placards shall be placed on
the fencing every 50 feet indicating the words, "NO TRESPASSING - Protected Trees". The
individual CRZ are a radius of one foot for each one inch of DBH (6 feet minimum), unless
otherwise delineated by WFCI (see Attachments #3 and 4).
Tree protection fences should be placed around the edge of the critical root zone (CRZ). 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 critical root zone. No
irrigation lines, trenches, or other utilities should be installed within the CRZ. 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 CRZ during construction, they should be cut cleanly with a
saw and covered immediately with moist soil. Noxious vegetation within the critical root zone
should be removed by hand. If a proposed save-tree must be impacted by grading or fills, 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
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.
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. 11 trees are proposed to be retained on the site in the buildable area.
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. 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 for
retention.
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4. Install tree protection fences along the 'limits of construction'. The fences should be located
at the limits of construction or 5 feet outside of the dripline of the save tree or as otherwise
specified by WFCI. Maintain fences throughout construction.
5. Complete 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. Complete clearing of the project.
7. Do not excavate stumps within 10’ of trees to be saved. These should be individually
evaluated by WFCI to determine the method of removal.
8. Complete all necessary pruning on save trees or stand edges to provide at least 8’ of ground
clearance near sidewalks and trails, and 15’ above all driveways or access roads.
9. Complete grading and construction of the project.
Summary
The City of Renton Municipal Code requires 11 of the 38 significant trees be retained on the
buildable area of the site. This plan retains 11 trees, which meets the minimum tree retention
requirement.
Please give me a call if you have further questions.
Respectfully submitted,
Washington Forestry Consultants, Inc.
Galen M. Wright, ASCA, ACF
ISA Board Certified Master Arborist PN-0129 BU
Certified Forester No. 44
ISA Tree Risk Assessor
attachments: aerial photo with forest cover types
site plan with tree protection areas
Tree maps with tree numbers and tree retention
tree list
individual tree condition rating key
description of tree evaluation methodology
glossary of forestry and arboricultural terms
tree protection fence detail
assumptions and limiting conditions
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Attachment #1: Aerial Photo of Vuecrest Site
with Forest Cover Types (King County Parcel Viewer 2.0)
Approximate Site Boundary
Planned Save Trees
NORTH
No Scale
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Attachment #2: Vuecrest Proposed Site Plan
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Attachment # 3. Tree locations with numbers and planned retention.
EAST HALF
WEST HALF
60 Matchline Matchline Tree Protection Fence Locations (Typ.)
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Attachment #4: Inventory list of project area trees
A detailed list of all trees by species, DBH, crown position, condition, root protection zone
(RPZ), drip line (D/L) radius, tree health status, and save/remove potential:
Tree Spp. DBH
Crown
Position
Tree
Condition RPZ
D/L
Radius
Healthy
Tree?
Save/
Remove
1 DF 12.3 S P-Topped 8 12 YES Remove
2 DF 17 C G 10 14 YES Save
3 DF 12.2 C G 8 12 YES Save
4 NS 24 D G 16 16 YES Save
5 CH 7 S VP 6 12 NO Remove
6 CH 10 S VP 8 16 NO Remove
7 CH 6 S VP 6 10 NO Remove
8 CH 8 S P 8 16 NO Remove
9 BM 4-8 S P 14 25 NO Remove
10 WP 14 C F 10 12 YES Remove
11 WP 13 S VP NO Remove
12 WP 14 C F 10 16 YES Remove
13 WP 22 C F 12 20 YES Remove
14 DF 18 C F 10 18 YES Remove
15 DF 26 C G 12 20 YES Remove
16 LP 8 S P 6 8 NO Remove
17 DF 24 C F 12 20 YES Remove
18 DF 16 C G 10 14 YES Remove
19 DF 38 D G 18 22 YES Remove
20 DF 32 D F 14 20 YES Remove
21 BL 3-7 C P 8 10 NO Remove
22 holly 6-8 P 8 8 NO Remove
23 apple 10 VP NO Remove
24 apple 8,6 VP NO Remove
25 apple 8,10 VP NO Remove
26 apple 10 VP NO Remove
27 DF 17 C F 12 18 YES Remove
28 DF 10 S F 8 8 YES Remove
29 DF 14 C F 10 14 YES Remove
30 WH 22 D F 12 20 YES Remove
31 DF 12 C G 12 15 YES Remove
32 DF 14 C G 12 18 YES Remove
33 BM 16,10 C F 12 20 YES Remove
34 DF 32 D F 14 22 YES Remove
35 BM 9 C P 10 12 NO Remove
36 BM 6 C P 8 10 NO Remove
37 BM 10-12 C P 12 16 NO Remove
38 BM 6-8 C P 12 15 NO Remove
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Tree Spp. DBH
Crown
Position
Tree
Condition RPZ
D/L
Radius
Healthy
Tree?
Save/
Remove
39 BM 4-10 C P 12 16 NO Remove
40 BM 7-10 C P 15 22 NO Remove
41 DF 35 D F 15 25 YES Remove
42 DF 14 C G 8 14 YES Save
43 DF 9 S F 6 10 YES Save
44 BM 6-10 D F 12 16 YES Save
45 BM 7-10 C P NO Remove
46 BM 10 C F 12 20 YES Save
47 BM 8-15 C P 12 20 NO
Remove
48 BM 8,14 C F 12 15 YES Save
49 BM 4-8 C P NO Remove
50 BM 16,18 C F 10 15 YES Remove
51 BM 4-6 C P NO Remove
52 BM 14-15 C F 12 25 YES Remove
53 BM 8-11 C F 10 15 YES Remove
54 DF 18 C F 12 18 YES Remove
55 DF 26 D F 15 20 YES Remove
56 BM 10 C VP NO Remove
57 BM 10 C F 8 12 YES Remove
58 BM 7 S F 6 10 YES Remove
59 BM
Off site
60 BM
Off site
61 BM 7-14 C F 12 15 YES Remove
62 BM 10 C F 8 12 YES Remove
63 BM 14 C F 10 12 YES Remove
64 BM 12,11 C P NO Remove
65 BM 16 D F 10 12 YES Remove
66 BM 7 S P 6 8 NO Remove
67 CB 7 S P NO Remove
68 BM 10-14 C P NO Remove
69 BM 12-14 C F 12 20 YES Remove
70 DF 24 D F 12 16 YES Remove
71 DF 11 S P 8 10 NO Remove
72 BM 12 C P NO Remove
73 BM 9 S VP NO Remove
74 DF 22 C VP NO Remove
75 BM 12 C VP NO Remove
76 DF 26 D F 12 15 YES Remove
77 BM 8-15 C P 12 18 NO Remove
78 RC 18 D VP NO Remove
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Tree Spp. DBH
Crown
Position
Tree
Condition RPZ
D/L
Radius
Healthy
Tree?
Save/
Remove
79 DF 9 C G 8 12 YES Remove
80 BM 16 D F 10 16 YES Remove
81 BM 18 D VP NO Remove
82 DF 20 D F 14 16 YES Remove
83 DF 13 C F 10 12 YES Remove
84 BM 20,18 C F 12 16 YES Remove
85 RC 14 S F 10 12 YES Remove
86 BM 12 C F 10 12 YES Remove
87 BM 11 C P 8 10 NO Remove
88 WH 6 S P NO Remove
89 DF 34 D F 12 18 YES Remove
90 DF 8 S P NO Remove
91 RC 10 S G 8 12 YES Remove
92 DF 12 S P NO Remove
93 RC 10 S F 8 12 YES Remove
94 BM
Off site
95 DF 7 S P 8 12 NO Remove
96 RC 11 S G 10 15 YES Remove
97 RC 6 S F 6 10 YES Remove
98 BM 10-14 C P 10 15 NO Remove
99 BM 8-12 C VP NO Remove
100 BM 10 S P NO Remove
101 BM 11 C F 8 12 YES Remove
102 BM 16 D F 10 15 YES Remove
103 BM 8-10 C VP NO Remove
104 BM 8 C VP NO Remove
105 BM 12 C dead NO Remove
106 BM 11 C F 10 10 YES Remove
107 BM 8,10 C F 10 14 YES Remove
108 BM 5-16 C F 10 14 YES Remove
109 BM 10,14 C F 10 14 YES Remove
110 BM 9 C F 10 12 YES Remove
111 BM 14,13 C P NO Remove
112 BM 12 C dead NO Remove
113 BM 13 C F 10 12 YES Remove
114 BM 8-12 C F 10 14 YES Remove
115 BM 13-17 D F 12 16 YES Save
116 BM 7 S F 6 8 YES Save
117 BM 14-23 D F 12 20 YES Save
118 BM 12,26 C F 12 15 YES Remove
119 DF 11 C F 8 10 YES Remove
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Tree Spp. DBH
Crown
Position
Tree
Condition RPZ
D/L
Radius
Healthy
Tree?
Save/
Remove
120 BM 8 C P NO Remove
Spp. = Species; DF = Douglas-fir; BM=bigleaf maple; WH = western hemlock; RC = western red cedar;
SS = Sitka spruce; NS = Norway spruce; CB = crabapple; CH = cherry.
Crown Position: D = Dominant; C = Co-dominant; I = Intermediate; S = Suppressed.
Tree Condition: VG = Very good; G = Good; F = Fair; P = Poor; VP = Very poor.
Note: some trees had multiple stems, thus a range of DBH's.
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Attachment #5: 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
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
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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 #6: 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 #7: 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).
Caliper: In the City of Renton - Caliper is referring to diameter measurement at DBH.
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 #8: Tree Protection Fence Detail
Temporary Chain Link on Driven Posts
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Attachment #9: 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 monitoring 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.