Applicant Arborist Report
Gardens of Fountainbleu Development
Cupertino, California
Prepared for:
Wald, Ruhnke & Dost Architects
Prometheus Real Estate Group, Inc.
Location:
10200 Miller Avenue
Cupertino, CA 95014
Prepared by:
Kevin Chisholm
ISA Certified Arborist WE-13243A
ArborMD Tree Care, Inc.
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Prepared by: ArborMD Tree Care, Inc. August 2023
Prepared for: Gardens of Fountainbleu & Prometheus Real Estate Group
Introduction
ArborMD tree care was asked to perform a development inventory on the trees at 10200 Miller
Avenue, Cupertino, CA 95014. The inventory was built per the requirements of the City of
Cupertino for the purposes of a planning application on behalf of Wald, Ruhnke, and Dost
Architects and Prometheus Real Estate Group. This report details the health, size, and
location of the trees and discusses tree protection and retention measures to meet the client’s tree
preservation intent. Per the requirements of the City of Cupertino, each tree on site must be
identified for species, diameter at breast height (54” above ground) measurement, height and
health condition.
Limits of the Assignment
Many factors can limit specific and accurate data when performing evaluations of trees, their
conditions, and values. The determinations and recommendations presented here are based on
current data and conditions that existed at the time of the evaluation and cannot be a predictor of
the ultimate outcomes for the trees. A visual inspection was used to develop the findings,
conclusions, and recommendations found in this report. Values were assigned to grade the
attributes of the trees, including structure and canopy health, and to obtain an overall condition
rating. No physical inspection of the upper canopy, sounding, root crown excavation, and
resistograph or other technologies were used in the evaluation of the trees.
Methods
Data was collected by an ISA Certified Arborist (Kevin Chisholm #WE-13243A). A visual
inspection was used to develop the findings, conclusions, and recommendations found in this
report. Using a digital tablet to record information, the arborist visually assessed the tree and
recorded information January 27, 2023. An updated assessment was performed on August 11,
2023. The tree ID numbering was based on the mapping plan determined at the time of
mapping, August 22, 2023, and was updated during both the original visit and subsequent visits
previously mentioned. Additional trees on site were assigned letters to disambiguate from trees
identified in the site plan.
The following attributes were collected:
Tree Tag: Tags were recorded based on mapping tool, ArborNote.
Species: Tree genus and species was identified.
Diameter at Breast Height (DBH): Trunk diameter was recorded to the nearest half-inch at 4.5
feet (breast height) above grade except where noted. When limbs or deformities occurred at
breast height, measurement was taken below 4.5.
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Prepared by: ArborMD Tree Care, Inc. August 2023
Prepared for: Gardens of Fountainbleu & Prometheus Real Estate Group
For multi-stemmed trees, the size was determined by measuring all the trunks, and then adding
the total diameter of the largest trunk to one-half the diameter of each additional trunk.
Height: Tree height was estimated in ten-foot increments.
Crown Spread: Approximate crown diameter was estimated by pacing parallel to the ROW.
Condition: The arborist evaluated the structure and health of the tree compared to other trees in
urban landscapes. Excellent, good, fair, poor, or dead were used to describe condition.
Notes: Additional observations, comments, or other points of consideration.
Observations
Site Observations
The site is a multi-family housing complex with single family, multi-family, and public
properties adjacent. Miller Ave to the southwest is a street with frequent traffic. The grade is flat.
Irrigation is present in all bed and turf areas where trees are located, but the spread and location
was not verified.
Map 1. Site Overview
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Tree Observations
Thirty-seven (37) trees were assessed on the site. Species included Mexican Fan Palm
(Washingtonia robusta, 13 trees), Common Juniper (Juniperus communis, 9), Sweet Gum
(Liquidambar, 6), and others. Tree condition ranged from poor (9) to good (8). Diameters at
breast height (DBHs) ranged from 1-36”, heights ranged from 6-35’.
Table 1. Trees on Site in Development Area
ID Common Name
Scientific Name DBH Height
Condition
Crown Spread (ft)
35 Sweet Gum
Liquidambar 16" 35’
Fair
20’
36 Sweet Gum
Liquidambar 14" 35’
Fair
18’
37 Sweet Gum
Liquidambar 19" 35’
Fair
22’
39 Mexican Fan Palm
Washingtonia robusta 19" 25’
Good
16’
41 Common Juniper
Juniperus communis 11" 15’
Fair
16’
42 Common Juniper
Juniperus communis 18" 15’
Fair
18’
43 Common Juniper
Juniperus communis 29" 10’
Fair
24’
44 Queen Palm
Syagrus romanzoffiana 9” 6’
Fair
5’
45 Tulip Poplar
Liriodendron tulipifera 35" 30’
Poor
30’
46 Tulip Poplar
Liriodendron tulipifera 36” 30’
Fair
20’
51 Sweet Gum
Liquidambar 24” 35’
Poor
20’
58 Crape Myrtle
Lagerstroemia 4" 15’
Good
12’
59 Crape Myrtle
Lagerstroemia 5" 15’
Good
8’
63 Sweet Gum
Liquidambar 3" 15’
Good
9’
120 Southern Magnolia
Magnolia grandiflora 26” 25’
Good
25’
121 Silver Dollar Gum
Eucalyptus polyanthemos 7” 15’
Poor
14’
122 Silver Dollar Gum
Eucalyptus polyanthemos 12” 15’
Poor
16’
123 Silver Dollar Gum
Eucalyptus polyanthemos 11" 15’
Poor
16’
124 Crape Myrtle
Lagerstroemia 3" 12’
Fair
7’
125 Southern Magnolia
Lagerstroemia 25” 30’
Fair
32’
133 Crape Myrtle
Lagerstroemia 1" 10’
Fair
5’
134 Cherry Laurel
Prunus laurocerasus 8" 10’
Fair
7’
135 Crape Myrtle
Lagerstroemia 3" 12’
Fair
6’
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Prepared by: ArborMD Tree Care, Inc. August 2023
Prepared for: Gardens of Fountainbleu & Prometheus Real Estate Group
ID Common Name
Scientific Name DBH Height
Condition
Crown Spread (ft)
136 Crape Myrtle
Lagerstroemia 5" 15’
Good
14’
137 Japanese Maple
Acer palmatum 9" 15’
Poor
15’
138 Crape Myrtle
Lagerstroemia 10” 15’
Good
15’
140 Crape Myrtle
Lagerstroemia 9” 12’
Good
12’
144
Japanese Flowering
Cherry
Prunus serrulata 12" 12’
Dead
7’
145 Rose of Sharon
Hibiscus syriacus 8" 7’
Poor
13’
168 Common Juniper
Juniperus communis 23” 20’
Fair
16’
169 Common Juniper
Juniperus communis 11” 20’
Fair
13’
170
Common Juniper
Juniperus communis
8” 18’
Fair
12’
171 Common Juniper
Juniperus communis 7” 20’
Fair
19’
172 Common Juniper
Juniperus communis 14” 20’
Fair
20’
173 Common Juniper
Juniperus communis 9” 20’
Fair
20’
188 Sweet Gum
Liquidambar 24” 35’
Poor
20’
189 Tulip Poplar
Liriodendron tulipifera 36” 30’
Poor
20’
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Prepared by: ArborMD Tree Care, Inc. August 2023
Prepared for: Gardens of Fountainbleu & Prometheus Real Estate Group
Recommendations
In performing our onsite survey, 37 development trees were inventoried, with the most prominent species being Common Juniper (9)
at 24% of the total count and Sweet Gum (6) at 16% of the total count. All but one Japanese Flowering Cherry on site were found to
be alive to be in poor, fair, and good condition. Of the 9 Common Juniper trees found on site, all were found to be in fair condition,
showing sign of improper pruning and drought stress. The Southern Magnolia (ID 120) showed evidence of significant scorching on
the trunk. Southern Magnolia’s that are not part of the potential removal plan will require annual mulching and excessive water to
supplement the effects of drought restrictions. In total, twenty-nine (29) trees are proposed to be removed (outlined in red on Table 1).
The following assessment was made regarding the trees to be removed.
1. Tree IDs (INSERT NUMBERS) will be heavily impacted by construction. The specific species are highlighted with red text
inventoried on pages 4-5. They are identified for removal. Tree ID 144 is dead and is to be removed.
2. The other trees on site are identified for preservation with arborist supervision. Supplemental irrigation through drip hose with
inline emitters should be applied May - October to support tree retention and health in the construction period. Irrigation
should be continued for other already irrigated landscaping.
3. The City’s standard root protection zone signs shall be affixed to the fencing every 30 feet. The ideal location for the fence is
outside of or along the RPZ. If no other alternative exists, fencing should be placed at the furthest extent of construction and
moved outward, away from the tree, as construction is completed. See appendix for maps. Please circle “Prescriptive” on the
sign.
a. Exception 1: If low branches preclude standard fencing, rather than raise canopies, T-posts with 4’ tall orange or green
plastic construction mesh may be used.
b. Exception 2: Tree protection fence may not block any secondary or emergency egress for the adjacent building, which
may include patios facing the street. Marked exits with signage excluding construction access on construction A-Frame
barricades are recommended.
All trees not being removed will need to be protected with fencing as outlined in Municipal Code 14.18 Appendix A “Standards for the
Protection of Trees During Grading and Construction Operations” in order to maintain sufficient barriers for preservation. Trees listed as
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Prepared by: ArborMD Tree Care, Inc. August 2023
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needing this protection are Tree ID#s: 44, 46, 51, 120, 138, 140, 188, and 189. Additionally, all tree protection will be based on the city
of Cupertino Tree Protection Conditions as listed in the “Cupertino Municipal Code 14.18.200 and 14.18.210”. Finally, trees noted for
removal do not fall under Municipal Code 14.18.050 “Protected Trees” designation.
Root Calculations:
This analysis considers two types of roots.
1. Structural roots near the trunk that should not be damaged or cut - Removal of these large anchoring roots can lead to structural
instability or failure.
2. Absorptive and feeder roots - These may be impacted with arborist supervision and monitoring. Removal (or compaction in the
area) of the feeder roots can cause immediate water stress, limit a trees’ ability to combat decay pathogens, and cause significant
declines in condition. The ability of a tree to survive root loss is dependent on its tolerance of drought, tree health, and the ability to
form new roots quickly. This area is called the Root Protection Zone. The trunk diameter (DBH) of each assessed tree was used to
determine the Root
Protection Zone (RPZ). The RPZ is considered the ideal preservation area of a tree. It is equal to 1 foot of radius for every inch of
trunk diameter measured at 4.5 feet from grade. The RPZ represents the typical rooting area required for tree health and survival.
Construction activities should be limited near or in the RPZ of any tree to be retained. This includes but is not limited to the storage of
materials, parking of vehicles, contaminating soil by washing out equipment, (concrete, paint, etc.), or changing soil grade. Like the
RPZ, the Structural Root Zone (SRZ) was also calculated using a commonly accepted method established by Dr. Kim Coder in
Conserving Trees During Site Development: A training manual. In this method, the root plate size (i.e. pedestal roots, zone of rapid
taper area, and roots under compression) and limit of disruption based upon tree DBH is calculated. The SRZ is the trunk radius at
breast height multiplied by 10.8. Significant risk of catastrophic tree failure exists if structural roots within the SRZ are cut, destroyed
or severely damaged. The SRZ is the area where no disturbance should occur unless by a Certified Arborist with Tree Risk
Assessment training. Please call Kevin Chisholm (207) 650-5736 to schedule monitoring site visits.
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Prepared by: ArborMD Tree Care, Inc. August 2023
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Tree Protection Recommendations:
The trees on site are identified for preservation with arborist supervision. Supplemental irrigation through drip hose with inline
emitters should be applied May - October to support tree retention and health in the construction period. Irrigation should be
continued for other already irrigated landscaping. Trees have been recently mulched, and the mulch should remain throughout
construction. The fence shall be 6 foot tall steel fencing mounted on 2 inch steel poles or t-posts driven 2 feet into the ground spaced
no more than 10 feet apart, or mounted in metal fence stands secured to the ground. The standard root protection zone signs shall be
affixed to the fencing every 30 feet. The ideal location for the fence is outside of or along the RPZ. If no other alternative exists,
fencing should be placed at the furthest extent of construction and moved outward, away from the tree, as construction is completed.
Please circle “Prescriptive” on the sign.
a. Exception 1: If low branches preclude standard fencing, rather than raise canopies, T-posts with 4’ tall orange or green
plastic construction mesh may be used.
b. Exception 2: Tree protection fence may not block any secondary or emergency egress for the
adjacent building, which may include patios facing the street.
Due to the sensitive nature of working within the RPZ of trees to be retained, ALL demolition, excavation or grading within the RPZ
of the trees must be performed with hand or pneumatic excavation tools and supervised by a Certified Arborist to monitor and
document any tree impacts. If root pruning is required of ROW trees a root pruning permit may be required. Any significant roots
(roots 2 inches in diameter or larger) encountered should be cut cleanly and photo documented under the supervision of the project
arborist. If severed roots increase failure risk beyond the property owner’s tolerance, the Arborist may recommend tree removal.
Efforts to reduce soil compaction and disturbance throughout the site should be implemented. No equipment should be driven on soil
areas, but be confined to paved surfaces throughout the project. Prior to installation of fill dirt behind the wall, mulch should be raked
back to avoid creating a hydrophobic layer. The fill material should be well drained sandy loam with organic material or compost
included. Wherever possible fill should be minimized, as fill material can suffocate and kill established tree roots. No material shall be
stored, nor concrete basins, painting equipment washed, or any chemical materials stored within the RPZ of the tree, and no
construction chemicals or paint should be released into landscaped areas, as these can be toxic to the tree and contaminate soil. A
Certified Arborist should inspect the trees on construction completion, and immediately if any changes in tree health, condition or
structural stability develop. If the trees decline, they should be monitored monthly or more frequently.
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Tree Protection Practices Per Sec. 14.18.200 and 14.18.210 - Protection of trees during construction:
Protected trees and other trees/plantings required to be retained by virtue of a development application, building permit, or tree
removal permit shall be protected during demolition, grading and construction operations. The applicant shall guarantee the protection
of the existing tree(s) on the site through a financial instrument acceptable to the Director of Community Development.
(Ord. 14-2126, § 3 (part), 2014; Ord. 13-2107, § 2 (part), 2013; Ord. 2085, § 2 (part), 2011; Ord. 2003, 2007; Ord. 1543, § 10.1, 1991)
A. A plan to protect trees described in Section 14.18.200 shall be submitted to the Director of Public Works and to the Director of
Community Development prior to issuance of a demolition, grading or building permit. The plan shall be prepared and signed by a
licensed landscape architect or arborist certified by the International Society of Arboriculture and shall be approved by the Director of
Community Development. The Director of Community Development shall evaluate the tree protection plan based upon the tree
protection standards contained in Appendix A at the end of this chapter.
B. The Director of Community Development may waive the requirement for a tree protection plan both where the construction
activity is determined to be minor in nature (minor building or site modification in any zone) and where the proposed activity will not
significantly modify the ground area within the drip line or the area immediately surrounding the drip line of the tree. The Director of
Community Development shall determine whether the construction activity is minor in nature and whether the activity will
significantly modify the ground area around the tree drip line.
(Ord; 14-2126, § 3 (part), 2014; Ord. 13-2107, § 2 (part), 2013; Ord. 2085, § 2 (part), 2011; Ord. 2003, 2007; Ord. 1543, § 10.2, 1991)
This report has identified proposed tree protection fencing within an assumed DIA (development impact area) If additional areas of the
site must be accessed for material storage or traversed by construction personnel or equipment, that information must be provided to
TCG fore review and integration into this report.
This report focuses on recommendations for tree preservation, and provides the RPZs and SRZs of these trees for
planning purposes. TCG has provided general preservation recommendations based on client-provided drawings,
but grading and drainage plans have not been reviewed.
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Figure 1. Tree Protection Zone
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Tree Canopy — Replacement Standard
A. Tree replacement:
1. The approval authority may impose the following replacement standards for approval of each tree to be removed in
conjunction with an approved tree removal permit, unless deemed otherwise by the approval authority. Table 14.18.160A may be used
as a basis for this requirement.
Table 14.18.160A - Replacement Tree Guidelines
Diameter of Trunk Size of Removed Tree (Measured 4½ feet
above grade)
Replacement Trees
Up to 12 inches* One 24" box tree
Over 12 inches and up to 18 inches Two 24" box trees or One 36" box
tree
Over 18 inches and up to 36 inches
Over 36 inches One 36" box tree
Heritage tree One 48" box tree
* Does not apply to R1, A1, A, RHS, and R2 zones except required privacy plantings trees in R1 zones
2. The approval authority shall work with the applicant/property owner of the tree removal permit to determine the location of the
replacement tree(s).
B. In lieu fees. The following provisions apply to all zones unless otherwise noted below:
1. If a replacement tree cannot reasonably be planted on the subject property as determined by a certified arborist, an in-lieu fee
shall be paid by the person requesting the tree removal permit. Fees shall be paid to the City’s Tree Fund to:
a. Add or replace trees on public property in the vicinity of the subject property; or
b. Add trees or landscaping on other City property.
2. The in-lieu fee for a mature specimen tree with trunk size equal to or less than thirty-six inches, shall be based upon the
purchase and installation cost of the replacement tree as determined by the Director of Community Development.
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3. The in-lieu tree replacement fee for a heritage tree or tree with a trunk size greater than thirty-six inches, shall be based upon the
valuation of the removed tree by using the most recent edition of the ISA Guide for Plant Appraisal published by the Council of Tree
and Landscape Appraisers.
4. If the subject property is within the R1, A1, A, RHS, and R2 zones, the person requesting the tree removal permit has the
option to pay the fee in-lieu of planting a replacement tree. Where the applicant would like to plant a replacement tree, but
demonstrates it is physically infeasible to plant on the subject property, the in-lieu fee shall be based on the purchase and installation
cost of the replacement tree as determined by the Director of Community Development. In cases where it is physically feasible to
plant, but the applicant chooses to pay the in-lieu fee instead of planting a replacement tree on the subject property, payment shall be
equivalent to one and one-half the calculated in-lieu tree replacement fee.
(Ord. 14-2126, § 3 (part), 2014; Ord. 13-2017, § 2 (part), 2013; Ord. 2085, § 2 (part), 2011)
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Table 2. Replacement Trees.
ID Common Name
Scientific Name Habitat Form
Height at Maturity
Crown Spread (ft)
Golden Rain Tree
Koelreuteria paniculata Flowering Tree
30’-40’
15’-30’
Crape Myrtle
Lagerstroemia miami Flowering Tree
20’
10’-15’
Crape Myrtle
Lagerstroemia miami Flowering Tree
20’
10’-15’
Crape Myrtle
Lagerstroemia miami Flowering Tree
20’
10’-15’
Crape Myrtle
Lagerstroemia miami Flowering Tree
20’
10’-15’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
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Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Queen Palm
Syagrus romanzoffiana Palm Tree
30’-40’
20’-25’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
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Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Chinese Windmill
Palm
Trachycarpus fortunei Palm Tree
20’-40’
10’-15’
Water Gum
Tristaniopsis laurina Evergreen Tree
15’-20’
15’-30’
Water Gum
Tristaniopsis laurina Evergreen Tree
15’-20’
15’-30’
Water Gum
Tristaniopsis laurina Evergreen Tree
15’-20’
15’-30’
Water Gum
Tristaniopsis laurina Evergreen Tree
15’-20’
15’-30’
Water Gum
Tristaniopsis laurina Evergreen Tree
15’-20’
15’-30’
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Map 2. Development Area
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Removal Photos:
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