Cities Index.
Agenda packet

Glendora City Council
January 24, 2023

Document
Agenda packet
Meeting
January 24, 2023
Body
Glendora City Council
Pages
35
Original file
375.1 MB
Text extracted from the city's file for reading and search. Open the original on meetings.ci.glendora.ca.us. That file is the official record.

5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated

8.5200e003 0.0728 0.0310 4.6000e- 004 5.8900e- 003 5.8900e- 003 5.8900e- 003 5.8900e- 003 92.9736 92.9736 1.7800e- 003 1.7000e- 003 93.5261 NaturalGasUnmitigated

8.5200e003 0.0728 0.0310 4.6000e- 004 5.8900e- 003 5.8900e- 003 5.8900e- 003 5.8900e- 003 92.9736 92.9736 1.7800e- 003 1.7000e- 003 93.5261

5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Page 22 of 27 Date: 3/18/2022 4:49 PM Glendora Hillside Subdivision - LST - South Coast AQMD Air District, Winter EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Item #8. Page 479
Meeting Date: 1/24/2023 / Packet Page #: 544

6.0 Area Detail

5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Other Asphalt
Surfaces
0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Single Family
Housing
790.276 8.5200e003 0.0728 0.0310 4.6000e- 004 5.8900e- 003 5.8900e- 003 5.8900e- 003 5.8900e- 003 92.9736 92.9736 1.7800e- 003 1.7000e- 003 93.5261 Total 8.5200e003 0.0728 0.0310 4.6000e- 004 5.8900e- 003 5.8900e- 003 5.8900e- 003 5.8900e- 003 92.9736 92.9736 1.7800e- 003 1.7000e- 003 93.5261 Unmitigated
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Other Asphalt
Surfaces
0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Single Family
Housing

0.790276 8.5200e003 0.0728 0.0310 4.6000e- 004 5.8900e- 003 5.8900e- 003 5.8900e- 003 5.8900e- 003 92.9736 92.9736 1.7800e- 003 1.7000e- 003 93.5261 Total 8.5200e003 0.0728 0.0310 4.6000e- 004 5.8900e- 003 5.8900e- 003 5.8900e- 003 5.8900e- 003 92.9736 92.9736 1.7800e- 003 1.7000e- 003 93.5261 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 23 of 27 Date: 3/18/2022 4:49 PM Glendora Hillside Subdivision - LST - South Coast AQMD Air District, Winter EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Item #8. Page 480
Meeting Date: 1/24/2023 / Packet Page #: 545

6.1 Mitigation Measures Area
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 1.2672 0.1807 1.0745 1.1300e003 0.0192 0.0192 0.0192 0.0192 0.0000 217.8104 217.8104 5.9200e- 003 3.9600e- 003 219.1386 Unmitigated 1.2672 0.1807 1.0745 1.1300e003 0.0192 0.0192 0.0192 0.0192 0.0000 217.8104 217.8104 5.9200e- 003 3.9600e- 003 219.1386 CalEEMod Version: CalEEMod.2020.4.0 Page 24 of 27 Date: 3/18/2022 4:49 PM Glendora Hillside Subdivision - LST - South Coast AQMD Air District, Winter EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Item #8. Page 481
Meeting Date: 1/24/2023 / Packet Page #: 546

6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating

0.1023 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

1.1142 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.0198 0.1692 0.0720 1.0800e003 0.0137 0.0137 0.0137 0.0137 0.0000 216.0000 216.0000 4.1400e- 003 3.9600e- 003 217.2836 Landscaping 0.0310 0.0115 1.0025 5.0000e005 5.5300e- 003 5.5300e- 003 5.5300e- 003 5.5300e- 003 1.8104 1.8104 1.7800e- 003 1.8550 Total 1.2672 0.1807 1.0745 1.1300e003 0.0192 0.0192 0.0192 0.0192 0.0000 217.8104 217.8104 5.9200e- 003 3.9600e- 003 219.1386 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 25 of 27 Date: 3/18/2022 4:49 PM Glendora Hillside Subdivision - LST - South Coast AQMD Air District, Winter EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Item #8. Page 482
Meeting Date: 1/24/2023 / Packet Page #: 547

7.1 Mitigation Measures Water

7.0 Water Detail

6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating

0.1023 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

1.1142 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.0198 0.1692 0.0720 1.0800e003 0.0137 0.0137 0.0137 0.0137 0.0000 216.0000 216.0000 4.1400e- 003 3.9600e- 003 217.2836 Landscaping 0.0310 0.0115 1.0025 5.0000e005 5.5300e- 003 5.5300e- 003 5.5300e- 003 5.5300e- 003 1.8104 1.8104 1.7800e- 003 1.8550 Total 1.2672 0.1807 1.0745 1.1300e003 0.0192 0.0192 0.0192 0.0192 0.0000 217.8104 217.8104 5.9200e- 003 3.9600e- 003 219.1386 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 26 of 27 Date: 3/18/2022 4:49 PM Glendora Hillside Subdivision - LST - South Coast AQMD Air District, Winter EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Item #8. Page 483
Meeting Date: 1/24/2023 / Packet Page #: 548

11.0 Vegetation

8.1 Mitigation Measures Waste8.0 Waste Detail9.0 Operational Offroad Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type

10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Page 27 of 27 Date: 3/18/2022 4:49 PM Glendora Hillside Subdivision - LST - South Coast AQMD Air District, Winter EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Item #8. Page 484
Meeting Date: 1/24/2023 / Packet Page #: 549
Grand Estates, City of Glendora Energy Demand
Scenario Vehicle MT CO2
Proposed Project Mobile Emissions 178.53
Fuel Type Vehicle MT CO2 Kg/CO2/Gallon Gallons
Proposed Project Gasoline 152.18 8.78 17,332
Proposed Project Diesel 26.35 10.21 2,581
19,913
Electricty and Natural Gas Demand
Electricity NG
Scenario kWh/yr kBtu/yr
Proposed Project 95,688 288,451
Mobile Source Petroleum Demand
Proposed Project Total
Item #8. Page 485
Meeting Date: 1/24/2023 / Packet Page #: 550
Appendix B-1
Biological Resources Technical Report
Item #8. Page 486
Meeting Date: 1/24/2023 / Packet Page #: 551
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DRAFT
Biological Resources Technical Report
Grand Estates Project
MARCH 2022
Prepared for:

CITY OF GLENDORA
Planning Department
116 E. Foothill Boulevard
Glendora, California 91741
Contact: Mark Carnahan
Prepared by:
38 North Marengo Avenue
Pasadena, California 92024
Contact: Michael Cady
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8375 i MARCH 2022
Table of Contents
SECTION PAGE NO.
1 Introduction ..........................................................................................................................................................1

1.1 Project Location......................................................................................................................................1

1.2 Project Description .................................................................................................................................1 2 Regulatory Setting................................................................................................................................................5

2.1 Federal ....................................................................................................................................................5

2.1.1 Federal Endangered Species Act.............................................................................................5

2.1.2 Migratory Bird Treaty Act..........................................................................................................5

2.1.3 Clean Water Act ........................................................................................................................5

2.2 State........................................................................................................................................................6

2.2.1 California Endangered Species Act..........................................................................................6

2.2.2 California Fish and Game Code ...............................................................................................6

2.2.3 California Environmental Quality Act .......................................................................................7

2.2.4 Porter–Cologne Water Quality Control Act ..............................................................................8

2.3 Local........................................................................................................................................................8

2.3.1 City of Glendora General Plan..................................................................................................8

2.3.2 City of Glendora Tree Preservation Ordinance No. 1768.......................................................9 3 Environmental Setting ...................................................................................................................................... 11

3.1 Climate................................................................................................................................................. 11

3.2 Soils...................................................................................................................................................... 11

3.3 Topography .......................................................................................................................................... 11

3.4 Land Uses ............................................................................................................................................ 12

3.4.1 On-Site Land Uses.................................................................................................................. 12

3.4.2 Surrounding Land Uses ......................................................................................................... 12

3.5 Watersheds and Hydrology ................................................................................................................. 12

3.6 Fire History........................................................................................................................................... 13 4 Methods............................................................................................................................................................. 15

4.1 Literature Review................................................................................................................................. 15

4.2 Resource Mapping .............................................................................................................................. 15

4.2.1 Vegetation Community and Land Cover Mapping ............................................................... 16

4.2.2 Flora and Fauna..................................................................................................................... 17

4.2.3 Focused Special-Status Plant Survey ................................................................................... 17

4.2.4 California Gnatcatcher Protocol Surveys.............................................................................. 17

4.2.5 Jurisdictional Delineation...................................................................................................... 18

4.2.6 Survey Limitations ................................................................................................................. 19

4.3 Special-Status Species Habitat Assessment..................................................................................... 19 Item #8. Page 490
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GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 ii MARCH 2022
5 Results............................................................................................................................................................... 21

5.1 Vegetation Communities, Land Covers, and Floral Diversity ............................................................ 21

5.1.1 Coast Live Oak Woodland ..................................................................................................... 21

5.1.2 California Walnut Groves....................................................................................................... 22

5.1.3 Disturbed California Sagebrush Scrub ................................................................................. 23

5.1.4 California Annual (Non-Native) Grassland............................................................................ 23

5.1.5 Urban/Developed .................................................................................................................. 24

5.1.6 Developed-Concrete Channel ............................................................................................... 24

5.1.7 Disturbed Land ...................................................................................................................... 25

5.1.8 Special-Status Vegetation Communities .............................................................................. 25

5.2 Floral Diversity ..................................................................................................................................... 25

5.3 Faunal Diversity ................................................................................................................................... 25

5.3.1 Amphibians and Reptiles ...................................................................................................... 25

5.3.2 Birds........................................................................................................................................ 25

5.3.3 Mammals ............................................................................................................................... 26

5.4 Special-Status Biological Resources.................................................................................................. 26

5.4.1 Special-Status Plant Species ................................................................................................ 26

5.4.2 Special-Status Wildlife Species............................................................................................. 27

5.5 Critical Habitat..................................................................................................................................... 29

5.6 Wildlife Corridors and Habitat Linkages............................................................................................. 30

5.7 Jurisdictional Delineation.................................................................................................................... 30

5.7.1 Summary of Jurisdictional Delineation Results ................................................................... 32

5.8 Regional Resource Planning............................................................................................................... 33

5.8.1 City of Glendora Tree Preservation Ordinance No. 1768.................................................... 33 6 Project Impacts ................................................................................................................................................. 35

6.1 Definition of Impacts........................................................................................................................... 35

6.1.1 Direct Permanent Impacts .................................................................................................... 35

6.1.2 Direct Temporary Impacts ..................................................................................................... 35

6.1.3 Indirect Impacts ..................................................................................................................... 35

6.1.4 Explanation of Findings of Significance................................................................................ 36

6.2 Impacts to Special-Status Species..................................................................................................... 37

6.2.1 Impacts to Special-Status Wildlife Species.......................................................................... 37

6.3 Impacts to Vegetation Communities and Land Covers......................................................................... 39

6.3.1 Direct Impacts........................................................................................................................ 39

6.3.2 Indirect Impacts ..................................................................................................................... 40

6.4 Impacts to Jurisdictional Waters ........................................................................................................ 40

6.4.1 Direct Impacts........................................................................................................................ 40

6.4.2 Indirect Impacts ..................................................................................................................... 41

6.5 Impacts to Wildlife Corridors and Habitat Connectivity........................................................................... 42 Item #8. Page 491
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GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 iii MARCH 2022

6.6 Regional Resource Planning............................................................................................................... 42

6.6.1 Direct Impacts........................................................................................................................ 42

6.6.2 Indirect Impacts ..................................................................................................................... 42 7 Mitigation........................................................................................................................................................... 45

7.1 Impact BIO-1: Special-Status Species................................................................................................ 45

7.2 Impact BIO-2: Sensitive Vegetation Communities............................................................................. 46

7.3 Impact BIO-3: Jurisdictional Wetlands and Waters ........................................................................... 48

7.4 Impact BIO-4: Habitat Linkages and Wildlife Corridors........................................................................... 50

7.5 Impact BIO-5: City of Glendora Protected Trees................................................................................ 50

7.6 Level of Significance After Mitigation................................................................................................. 51 8 References ........................................................................................................................................................ 53

APPENDICES
A Representative Site Photographs
B Plant Species Compendium
C Wildlife Species Compendium
D Assessment of Special-Status Plant Species Potentially Occurring in the Study Area E Assessment of Special-Status Wildlife Species Potentially Occurring in the Study Area F 2019 Focused California Gnatcatcher Survey 45-Day Report for the Grand Estates, City of Glendora, California G Jurisdictional Delineation Data
H Tree Information Matrix (2020), Tree Locations (2020), and Initial Tree Report (2019)

FIGURES
1 Project Location ................................................................................................................................................ 57 2 Tentative Tract Map No. 72413....................................................................................................................... 59 3 Hydrogeologic Setting ....................................................................................................................................... 61 4 Biological Resources......................................................................................................................................... 63 5 Coastal California Gnatcatcher ........................................................................................................................ 65 6 Potential Jurisdictional Waters......................................................................................................................... 67 7 Impacts to Biological Resources ...................................................................................................................... 69 TABLES
1 City of Glendora Replacement Criteria for Privately Owned Trees................................................................. 10 2 Soils on Grand Estates Site.............................................................................................................................. 11 3 Survey Dates and Conditions ........................................................................................................................... 16 4 Vegetation Communities and Land Covers within the Study Area................................................................. 21 Item #8. Page 492
Meeting Date: 1/24/2023 / Packet Page #: 557

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 iv MARCH 2022
5 Special-Status Wildlife Species Present or with Moderate or High Potential to Occur within the Study Area........................................................................................................................................ 27 6 Potential Jurisdictional Waters within the Study Area .................................................................................... 32 7 Protected Trees in the Study Area ................................................................................................................... 33 8 Permanent and Temporary Direct Impacts to Vegetation Communities and Land Covers .......................... 39 9 Direct Impacts to Potential Jurisdictional Waters ........................................................................................... 41 Item #8. Page 493
Meeting Date: 1/24/2023 / Packet Page #: 558
8375
v MARCH 2022
Acronyms and Abbreviations
Acronym/Abbreviation Definition
AMSL above mean sea level
BRTR Biological Resources Technical Report
CDFW California Department of Fish and Wildlife
CEQA California Environmental Quality Act
CESA California Endangered Species Act
CNDDB California Natural Diversity Database
CNPS California Native Plant Society
CRP Conceptual Restoration Plan
CRPR California Rare Plant Rank
FESA federal Endangered Species Act
HCP Habitat Conservation Plan
HMMP Habitat Mitigation and Monitoring Plan
LACFCD Los Angeles County Flood District
NCCP Natural Community Conservation Plan
OHWM ordinary high water mark
RWQCB Regional Water Quality Control Board
SSC Species of Special Concern
TPZ tree protection zone
USACE U.S. Army Corps of Engineers
USFWS U.S. Fish and Wildlife Service
Item #8. Page 494
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GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 vi MARCH 2022

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Item #8. Page 495
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8375 1 MARCH 2022
1 Introduction
Dudek has prepared this Biological Resources Technical Report (BRTR) for the City of Glendora (City) for the Grand Estates (proposed Project or Project). The Project proposes to develop 12 new single-family residential lots and one lot for two private streets located on privately owned land within the City of Glendora, Los Angeles County, California.

The Project site includes several flood control easements within the northern portion of the property. Thus, the proposed Project also includes the installation of three debris basins (per Los Angeles County Flood Control Department requirements) and construction of a new access road within the northern portion of the property.

The purpose of this report is to: (1) describe the conditions of biological resources within the Project area in terms of vegetation, flora, jurisdictional waters and wetlands, wildlife, and wildlife habitats; (2) quantify potential direct and indirect impacts to biological resources that will result from the proposed Project; (3) discuss those impacts in terms of biological significance in view of federal, state, and local laws and City policies; and (4) discuss mitigation measures that will reduce significant biological impacts to a less-than-significant level consistent with federal, state, and local regulations, including the California Environmental Quality Act (CEQA). This BRTR presents the findings of several biological surveys conducted at the Project site by Dudek, including a general biological reconnaissance survey conducted on May 15, 2019, jurisdictional delineation update on July 18, 2019, focused special-status bird surveys from April to July 2019, focused special-status plant surveys conducted in May and July 2019, and a general biological reconnaissance survey conducted on January 22, 2022.

1.1 Project Location
The approximately 27-acre property is located on privately owned land at 950 North Silent Ranch Drive within the City of Glendora in eastern Los Angeles County, approximately 23 miles east of downtown Los Angeles, as shown on Figure 1, Project Location. The general Project area lies north of I-210, east of SR-39, and west of SR-57 bordered by the Cities of Azusa to the west, San Dimas to the east, Citrus, Covina and Charter Oaks to the south, and unincorporated Los Angeles County to the north. The Project area is in Township 10 North, Range 6 West, and Section 4 as shown on the U.S. Geological Survey (USGS) 7.5-minute Glendora, CA and Azusa, CA quadrangle maps (USGS 2018). The northern approximately 16 acres of the property is zoned Open Space - Natural and are designated as a “building restriction area”, and the southern approximately 11 acres is zoned for single-family residences.

1.2 Project Description
The proposed Project would develop 12 new graded pads and a Private Street in the southern section of the Project site. Each residential lot would accommodate custom home development at a future date. One existing home and its associated residential lot is also included within the Project boundaries. Although the ultimate timing and design of each residential home would occur at an unknown future date subject to economic market conditions and the buyer’s preferences, for the purposes of the impact evaluation within this IS/MND, the construction and long-term occupancy of the properties is assumed and analyzed. The existing single-family residence in the southwestern corner of the Project site would remain in place. As such, upon buildout, the Project site is expected to support a total of 12 residences, all of which would be located within the 11-acre southern section of the Project site, which is zoned for single-family residential use.

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GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 2 MARCH 2022
The approximately 11-acre southern section of the site would be developed with residential uses and the approximately 16-acre northern section of the site would remain as open space, with the exception of flood control.

The new lots would range in size from approximately 32,000 square feet to 20,000 square feet. The existing singlefamily residence is on a 86,010 square foot lot.

The Private Street would be constructed along the southeastern edge of the Project site, providing access to each residential lot. The street would be privately held by the Homeowner’s Association (HOA), which would be established for the proposed development, once the new custom homes are constructed and occupied. More specifically, covenants, conditions, and restrictions of the HOA would be approved prior to grading so that all hydroseeding, watering, maintenance of the HOA areas and the habitat restoration areas; additional mitigation requirements; and other conditions or approvals would be established prior to construction of the proposed Project.

The City would impose this as a condition of approval of the Tentative Tract Map. Entrance to the Project site would be gated, with a gate controller and turn-around located within the Private Street adjacent to Lots 13 and 14.

Flood Control Facility Improvements
The northern 16 acres of the Project site are zoned open space and would be designated as a “building restriction area.” No habitable structures would be constructed within the northern section of the Project site, except for the proposed flood/debris control facilities. The LACFCD determined that with implementation of the proposed Project, potential debris flows during rain events from the undeveloped hillside areas to the north of the site could not be adequately captured by the existing debris control structures, which are filled to capacity and no longer function as intended. Therefore, the existing three flood control/debris check dam structures would be removed and larger flood/debris control facilities would be constructed within generally the same location, to protect the new residential development from safety hazards associated with flooding and debris flow.

Each spillway inlet would be approximately 5 feet tall, would include a debris barrier rack to filter out large woody debris, and would connect to a 36-inch reinforced concrete pipeline that would connect to the storm drain system in the residential area below. An asphalt maintenance access road would be constructed to the north of the residential development and to the south of the inlets and the debris basin, to allow maintenance vehicles to access the drainage facilities. The access road would be paved and would be 20 feet wide with 40-foot diameter turnarounds to allow for vehicular and maintenance equipment site ingress/egress and connect to the proposed Private Street. Ramps would be constructed from the access roads to the top of the earthen debris basins to allow for vehicle access.

Landscape and Fuel Modification Improvements
Retaining walls would be screened by shrubbery. Anticipated landscape trees include canyon live oak, black walnut, Brisbane box, hollyleaf cherry, and Chinese pistache. All on-site lots would be equipped with landscaping irrigation. A 6-foot masonry screen wall would be constructed on the eastern edge of the Tract Map, which would serve as aesthetic fencing but also as wildfire protection between the Project site and the adjacent residential uses to the east.

Areas adjacent to the proposed debris basins would be subject to minimal grading/grooming to remove loose surface materials and reduce loose debris from running off into the debris basin facilities, as required by the Item #8. Page 497
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GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 3 MARCH 2022
LACFCD. Upon completion of the Project, the affected slopes would be hydroseeded with native seeds to facilitate the reestablishment of vegetative cover.

Offsite Components
A subterranean water, sewer, and storm drain infrastructure are the only off-site features required for Project implementation. The trenching required for pipeline installation and connection to subterranean existing utility infrastructure would be within paved roadways/driveways. Storm drain improvements along Palm Drive would require trenching within the existing sidewalk. The sidewalk would be repaved once storm drain improvements are implemented, as a condition of approval for the Project.

Short-Term Construction Activities
The first phases of construction would consist of site preparation and grading. During grading, the total cut is anticipated to be approximately 93,000 cubic yards, and the total fill is anticipated to be approximately 96,500 cubic yards, with 2,300 cubic yards of imported soils required. This includes 73,000 cubic yards of cut materials and 32,000 cubic yards of fill materials within the debris basin infrastructure hillside area, and 20,000 cubic yards of cut materials and 64,500 cubic yards of fill materials within the residential development area. Construction activities would occur in one phase, and could take place Monday to Friday from 7:00 a.m. to 6:00 p.m., with no work allowed on Saturdays, Sundays, or federal holidays, with the exception of interior work.

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8375 5 MARCH 2022
2 Regulatory Setting
This chapter outlines the federal, state, and local regulations pertinent to the biological resources located on the Project site.

2.1 Federal

2.1.1 Federal Endangered Species Act
The federal Endangered Species Act (FESA) of 1973 (16 USC 1531 et seq.), as amended, is administered by the U.S. Fish and Wildlife Service (USFWS) for most plant and animal species and by the National Oceanic and Atmospheric Administration National Marine Fisheries Service for certain marine species. This legislation is intended to provide a means to conserve the ecosystems upon which endangered and threatened species depend and provide programs for the conservation of those species, thus preventing the extinction of plants and wildlife.

The FESA defines an endangered species as “any species that is in danger of extinction throughout all or a significant portion of its range.” A threatened species is defined as “any species that is likely to become an endangered species within the foreseeable future throughout all or a significant portion of its range.” Under FESA, it is unlawful to “take” any listed species, and “take” is defined as, “harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect, or to attempt to engage in any such conduct.” FESA allows for the issuance of incidental take permits for listed species under Section 7, which is generally available for projects that also require other federal agency permits or other approvals, and under Section 10, which provides for the approval of habitat conservation plans on private property without any other federal agency involvement.

2.1.2 Migratory Bird Treaty Act
The Migratory Bird Treaty Act (16 USC 703 et seq.), as amended, prohibits the intentional take of any migratory bird or any part, nest, or eggs of any such bird. Under the Migratory Bird Treaty Act, “take” is defined as pursuing, hunting, shooting, capturing, collecting, or killing, or attempting to do so. Additionally, Executive Order 13186, Responsibilities of Federal Agencies to Protect Migratory Birds, requires that any project with federal involvement address impacts of federal actions on migratory birds with the purpose of promoting conservation of migratory bird populations (66 FR 3853–3856). The Executive Order requires federal agencies to work with USFWS to develop a memorandum of understanding. USFWS reviews actions that might affect these species.

2.1.3 Clean Water Act
The Clean Water Act provides guidance for the restoration and maintenance of the chemical, physical, and biological integrity of the nation’s waters. Section 401 requires a project operator for a federal license or permit that allows activities resulting in a discharge to waters of the United States to obtain state certification, thereby ensuring that the discharge will comply with provisions of the Clean Water Act. The Regional Water Quality Control Boards (RWQCB) administer the certification program in California. Section 402 establishes a permitting system for the discharge of any pollutant (except dredged or fill material) into waters of the United States. Section 404 establishes a permit program administered by USACE that regulates the discharge of dredged or fill material into waters of the Item #8. Page 500
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United States, including wetlands. USACE implementing regulations are found at 33 CFR 320 and 330. Guidelines for implementation are referred to as the Section 404(b)(1) Guidelines, which were developed by the U.S.

Environmental Protection Agency in conjunction with USACE (40 CFR 230). The guidelines allow the discharge of dredged or fill material into the aquatic system only if there is no practicable alternative that would have less adverse impacts.

Wetlands and Other Waters of the United States
Aquatic resources, including riparian areas, wetlands, and certain aquatic vegetation communities, are considered sensitive biological resources and can fall under the jurisdiction of several regulatory agencies. USACE exerts jurisdiction over waters of the United States, including all waters that are subject to the ebb and flow of the tide; wetlands and other waters such as lakes, rivers, streams (including intermittent or ephemeral streams), mudflats, sandflats, sloughs, prairie potholes, vernal pools, wet meadows, playa lakes, or natural ponds; and tributaries of the above features.

The extent of waters of the United States is generally defined as that portion that falls within the limits of an ordinary high-water mark (OHWM). Typically, the OHWM corresponds to the water surface elevation of a 2-year flood event (USACE 2008a). In addition, waters of the United States may include wetlands, including swamps, bogs, seasonal wetlands, seeps, marshes, and similar areas, defined by USACE as “those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil conditions” (33 CFR 328.3[b]; 40 CFR 230.3[t]). Indicators of three wetland parameters (i.e., hydric soils, hydrophytic vegetation, and wetlands hydrology), as determined by field investigation, must be present for a site to be classified as a wetland by USACE (USACE 1987).

2.2 State

2.2.1 California Endangered Species Act
The California Endangered Species Act (CESA) (California Fish and Game Code, Section 2050 et seq.) provides protection and prohibits the take of plant, fish, and wildlife species listed by the State of California. Unlike FESA, under CESA state-listed plants have the same degree of protection as wildlife, but insects and other invertebrates may not be listed. Take is defined similarly to FESA and is prohibited for both listed and candidate species. Take authorization may be obtained by the Project applicant from CDFW under CESA Section 2081, which allows take of a listed species for educational, scientific, or management purposes. In this case, private developers consult with CDFW to develop a set of measures and standards for managing the listed species, including full mitigation for impacts, funding of implementation, and monitoring of mitigation measures.

2.2.2 California Fish and Game Code
Fully Protected Species
Sections 3511, 4700, 5050, and 5515 of the California Fish and Game Code outline protection for fully protected species of mammals, birds, reptiles, amphibians, and fish. Species that are fully protected by these sections may not be taken or possessed at any time. CDFW cannot issue permits or licenses that authorize the “take” of any fully protected species, except under certain circumstances, such as scientific research and live capture and relocation Item #8. Page 501
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of such species pursuant to a permit for the protection of livestock. Furthermore, it is the responsibility of the CDFW to maintain viable populations of all native species. Toward that end, the CDFW has designated certain vertebrate species as Species of Special Concern (SSC), because declining population levels, limited ranges, and/or continuing threats have made them vulnerable to extinction.

Section 1602
Under Section 1602 of the California Fish and Game Code, a Project operator is required to notify CDFW prior to any Project that would divert, obstruct, or change the natural flow, bed, channel, or bank of any river, stream, or lake. Pursuant to the code, a “stream” is defined as a body of water that flows at least periodically, or intermittently, through a bed or channel having banks and supporting fish or other aquatic life. Based on this definition, a watercourse with surface or subsurface flows that supports or has supported riparian vegetation is a stream and is subject to CDFW jurisdiction, with the jurisdictional limits extending beyond the top of bank to the outer canopy limits of riparian-associated vegetation that overlies the stream. Altered or artificial watercourses valuable to fish and wildlife are also subject to CDFW jurisdiction.

CDFW also has jurisdiction over dry washes that carry water during storm events.

Preliminary notification and Project review generally occur during the environmental process. When an existing fish or wildlife resource may be substantially adversely affected, CDFW is required to propose reasonable Project changes to protect the resource. These modifications are formalized in a Streambed Alteration Agreement, which becomes part of the plans, specifications, and bid documents for the Project.

California Native Plant Protection Act
The Native Plant Protection Act of 1977 (see Section 1900 et seq. of the California Fish and Game Code) directed CDFW to carry out the Legislature’s intent to “preserve, protect and enhance rare and endangered plants in this State.” The Native Plant Protection Act gave the California Fish and Game Commission the power to designate native plants as “endangered” or “rare” and protect endangered and rare plants from take. CESA expanded on the original Native Plant Protection Act and enhanced legal protection for plants, but the Native Plant Protection Act remains part of the California Fish and Game Code. To align with federal regulations, CESA created the categories of “threatened” and “endangered” species. It converted all “rare” animals into the act as threatened species, but did not do so for rare plants. Thus, there are three listing categories for plants in California: rare, threatened, and endangered. Because rare plants are not included in CESA, mitigation measures for impacts to rare plants are specified in a formal agreement between CDFW and the Project Applicant.

Nesting Birds
Section 3503 makes it unlawful to take, possess, or needlessly destroy the nest or eggs of any bird and Section 3513 makes it unlawful to take or possess any migratory nongame bird as designated in the MBTA.

2.2.3 California Environmental Quality Act
CEQA requires identification of a Project’s potentially significant impacts on biological resources and ways that such impacts can be avoided, minimized, or mitigated. The act also provides guidelines and thresholds for use by lead agencies for evaluating the significance of proposed impacts.

CEQA Guidelines Section 15380(b)(1) defines endangered animals or plants as species or subspecies whose “survival and reproduction in the wild are in immediate jeopardy from one or more causes, including loss of habitat, Item #8. Page 502
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change in habitat, overexploitation, predation, competition, disease, or other factors.” A rare animal or plant is defined in Section 15380(b)(2) as a species that, although not presently threatened with extinction, exists “in such small numbers throughout all or a significant portion of its range that it may become endangered if its environment worsens; or … [t]he species is likely to become endangered within the foreseeable future throughout all or a significant portion of its range and may be considered ‘threatened’ as that term is used in the federal Endangered Species Act.” Additionally, an animal or plant may be presumed to be endangered, rare, or threatened if it meets the criteria for listing, as defined further in CEQA Guidelines Section 15380(c).

CDFW has developed a list of “Special Species” as “a general term that refers to all of the taxa the California Natural Diversity Database (CNDDB) is interested in tracking, regardless of their legal or protection status.” This is a broader list than those species that are protected under the FESA, CESA, and other California Fish and Game Code provisions, and includes lists developed by other organizations, including for example the Audubon Watch List Species. Guidance documents prepared by other agencies, including the Bureau of Land Management Sensitive Species and USFWS Birds of Special Concern, are also included on this CDFW Special Species list. Additionally, CDFW has concluded that plant species listed as California Rare Plant Rank (CRPR) 1 and 2 by the California Native Plant Society (CNPS 2022a), and potentially some CRPR 3 plants, are covered by CEQA Guidelines Section 15380.

Section IV, Appendix G (Environmental Checklist Form), of the CEQA Guidelines requires an evaluation of impacts to “any riparian habitat or other sensitive natural community identified in local or regional plans, policies, regulations, or by the California Department of Fish and Wildlife or the U.S. Fish and Wildlife Service.”

2.2.4 Porter–Cologne Water Quality Control Act
The intent of the Porter–Cologne Water Quality Control Act is to protect water quality and the beneficial uses of water, and it applies to both surface water and groundwater. Under this law, the State Water Resources Control Board develops statewide water quality plans, and the nine RWQCB develop basin plans that identify beneficial uses, water quality objectives, and implementation plans. The RWQCB have the primary responsibility to implement the provisions of both statewide and basin plans. Waters regulated under the Porter–Cologne Water Quality Control Act include isolated waters that are no longer regulated by USACE. Developments with impact to jurisdictional waters must demonstrate compliance with the goals of the act by developing stormwater pollution prevention plans, standard urban stormwater mitigation plans, and other measures to obtain an order of Waste Discharge Requirement (or, in cases where a CWA Section 401 certification is required, a waiver of Waste Discharge Requirement).

2.3 Local

2.3.1 City of Glendora General Plan
The following policies of the Land Use and Natural Resource Conservation Elements of the City of Glendora General Plan (2006) are relevant to naturally occurring biological resources:
▪ Goal CON-9: Preservation and conservation of natural resources and sensitive habitats. - CON-9.1 Investigate opportunities for open space land acquisition for the preservation of natural resources and sensitive habitats.

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- CON-9.2 Continue to partner with the Glendora Community Conservancy to determine funding opportunities for open space land acquisitions for the preservation of natural resources and sensitive habitats. - CON-9.3 Pursue partnerships with other organizations, such as the United States Forest Service to ensure preservation of natural resources and sensitive habitats. - CON-9.4 Ensure the preservation of the natural plant communities in the hillside areas. - CON-9.5 Ensure land use decisions consider the preservation of sensitive plant and animal species, critical habitat, wildlife corridors, and biologically sensitive areas. - CON-9.6 Develop a land management/land maintenance plan, including best management practices, of City-owned conservation areas to increase fire safety, protect biodiversity and preserve native plant species.
- CON-9.7 Ensure preservation of local watersheds in development to maintain native plant habitats and ensure connectivity of wildlife corridors.
▪ Goal CON-10: A tree preservation strategy
o CON-10.1 Involve residents in the maintenance and preservation of individual trees by providing them with a choice of trees planted.
o CON-10.2 Maintain the tree preservation ordinance to ensure the preservation of existing tree resources. o CON-10.4 Ensure appropriate placement and proper maintenance of tree resources within the City.

The City of Glendora defines vegetation communities to be sensitive if they provide habitat for listed or otherwise sensitive species, are of special value to the local ecosystem (e.g., water sources), or are regulated by local, State or federal resources agencies (City of Glendora 2006a). Woodland habitats, particularly along streambeds, are recognized as being highly sensitive habitats because major drainages that contain woodland habitat support a wide diversity of wildlife species and may function as habitat linkages and corridors. Additionally, coastal sage scrub is considered a sensitive vegetation community based on extensive loss of habitat and widespread awareness among the resource agencies, policy makers, and public (City of Glendora 2006a). Woodland and coastal sage scrub habitats are considered special-status vegetation communities in this report based on their local importance as defined in the Glendora Community Plan (City of Glendora 2006a).

2.3.2 City of Glendora Tree Preservation Ordinance No. 1768 In accordance with Tree Preservation Ordinance No. 1768 (City of Glendora 2003), Section 20.08.130(6) requires that all existing living trees meeting the requirements in the Urban Forestry Manual (City of Glendora 2018aa), be preserved to the extent feasible as per recommendations provided by a certified arborist. If trees are destroyed, the applicant shall replace them with suitable trees in locations determined by the Planning Department before final occupancy is granted to any new resident. Additionally, where required by the Planning Department, the applicant shall submit a tree preservation/relocation/replacement/removal plan, which shall include the methods of tree preservation, tree replacement recommendations, and a report with recommendations from a certified arborist, as per the guidelines outlined in Tree Preservation Ordinance No. 1768 (City of Glendora 2003).

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The Urban Forestry Manual defines policies and procedures utilized by City staff in the management and care of all trees located on City owned property, with City parkway areas, in some cases regarding California native species, and new developments (e.g., private property) (City of Glendora 2018a). The City takes impacts on private property trees into consideration with every application for discretionary zoning approval in order to maintain and further develop the local urban forest on public and private property within the City (City of Glendora 2018a). Removal of any species of private trees with a diameter at breast height (DBH) of 10 inches or more must be replaced according to the size scale described in the Urban Forestry Manual (City of Glendora 2018a).

Native oak trees are of particular importance within the City of Glendora. Any oak removed from private property with a DBH of 8” or more, as well as multi-trunk trees, oak or other species with a combined DBH of all trunk branches 4” DBH or greater shall require replacement as per the Urban Forestry Manual (City of Glendora 2018a), as shown in Table 1, City of Glendora Replacement Criteria for Privately Owned Trees. Additionally, the addendum to Chapter 16.12 of the City of Glendora tree preservation ordinance protects pre-existing or native trees that may be impacted by new development in the City (City of Glendora 2003, 2018). It is the City’s policy to protect and preserve healthy trees that provide valuable benefits to the environment and quality of life in Glendora (City of Glendora 2003, 2018).

Table 1. City of Glendora Replacement Criteria for Privately Owned Trees Tree to be
Removed Tree
Existing Diameter at Breast
Height (DBH)
Container
Replacement Size
Any species with a
DBH of at least 10
inches
10 to 15 inches 24-inch boxed tree - 1:1 replacement
15 to 36 inches 36-inch boxed tree - 1:1 replacement
36 to 48 inches 48-inch boxed tree - 2:1 replacement
49 inches or more To be determined by the City Forester Native oak trees with
DBH of at least 8
inches
8 to 15 inches 36-inch boxed tree - 2:1 replacement
15 to 36 inches 48-inch boxed tree - 3:1 replacement
36 inches or more To be determined by the City Forester Item #8. Page 505
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3 Environmental Setting
The purpose of this chapter is to describe the general existing conditions within and adjacent to the Study Area to document the baseline conditions for the BRTR and subsequent analysis.

3.1 Climate
The Project site is located approximately 35 miles from the Pacific Ocean. The City of Glendora has a Mediterranean climate with cool, wet winters and hot, dry summers. August is the average warmest month with an average high temperature of 92 degrees Fahrenheit (˚F) and December is the coolest month on average with a low of 42 ˚F.

Rainfall occurs primarily between October and April, with the maximum average precipitation occurring in January.

According to the Western Regional Climate Center (WRCC) (2022), the mean annual rainfall for the region is 14.39 approximate inches of rain per year.

3.2 Soils
Soils mapping is from the County of Los Angeles, using the U.S. Department of Agriculture (USDA) National Resources Conservation Service (NRCS) Soil Survey Geographic database (County of Los Angeles 2014). Soils and their acreages are provided in Table 2, Soils on Grand Estates Site, spatial distributions are presented within Figure 3, Hydrogeologic Setting, and a brief description of each soil series is provided below.

Table 2. Soils on Grand Estates Site
Soil Mapping Unit Acres
Hanford Gravelly Sandy Loam 6.9
Upper San Gabriel River 20.0
Source: County of Los Angeles 2014.

Note: Numbers may not sum due to rounding.

Hanford gravelly sandy loam occurs within the southern portion of the Project area. This soil is well-drained and formed from moderately fine textured consolidated alluvium, soft shale, and fine grained sandstone. This soil is formed from alluvium dominantly from granite and other quarts rocks and occurs on floodplains, stream bottoms and alluvial fans.

The Hanford series are well-drained soils with low runoff and rapid permeability (USDA NRCS 2022a).

Upper San Gabriel River. Limited information is available for the upper San Gabriel river soils series. According to the Final Program Environmental Impact Report for the San Gabriel River Corridor Master Plan (County of Los Angeles 2006), the primary soils found within the upper San Gabriel river watershed consist of silt loam and sand.

3.3 Topography
On-site elevations range from 960 feet above mean sea level (AMSL) to 1,170 feet AMSL. The southern portion of the site, where development is proposed, is slightly south sloping and has a moderate to flat grade. Elevations across this portion of the site range from 960 to 1,025 AMSL. The northern approximately 16 acres, which are designated as preserve open space, contain moderate to steep slopes with elevations ranging from 1,026 feet to 1,170 feet AMSL.

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3.4 Land Uses

3.4.1 On-Site Land Uses
The Project area is located along the foothills and hillsides of the San Gabriel Mountains. The Project area is largely undeveloped, with the exception of an existing single-family residential lot that is located along the southwestern portion of the Project site and zoned for development. The ground surface has been previously disturbed within the majority of the level areas zoned for single-family residential development and use. This area has been used as a Girl Scout camp and for various other outdoor uses. The northern portion of the Project area zoned as open space is comprised of moderate to steep slopes consisting of undeveloped canyons lined with coast live oak woodland and California walnut groves. Additionally, non-native grassland and disturbed California sagebrush scrub habitat occurs along the ridges of the mountains.

The Project is within the Low Density Residential Land Use Designation within the City of Glendora (City of Glendora 2018b). The Low Density Residential Designation is provided for transitional areas between hillside areas and higher density single-family residential areas and allows for the development of single family residential on lots ranging from 10,500 to 30,000 square feet (City of Glendora 2006b). The Project is within the Hillside Study Area and consistent with the Recommended Hillside Strategy document (City of Glendora 2006b). Based upon Dudek’s review of the General Plan, the Project would not conflict with any City goals, policies, and/or design.

3.4.2 Surrounding Land Uses
To the north of the Project site are mountainous, undeveloped areas within the northern portion of the City.

Approximately 0.31 mile to the north is the southern boundary of the Angeles National Forest. To the east of the Project site are hillside areas (also within the City of Glendora) that are sparsely developed with rural residences. (This area is designated as “Hillside Very Low Density” in the City’s General Plan.) The areas south and southwest of the Project site are developed with single-family residential neighborhoods. Approximately 0.15-mile southwest of the Project site is St. Lucy’s Priory High School. To the southwest of the Project site is also a small unincorporated area of the County, which is surrounded on all sides by the City of Glendora. This area is developed primarily with single-family residences. To the west of the Project site are single-family residences, undeveloped hillside areas within the City, and utility and flood control infrastructure, consisting of a concrete drainage system that leads out of the San Gabriel Mountains. Also to the west of the Project site is the Church of the Open Door, located approximately 0.15-mile west of the Project site.

Several County-designated Significant Ecological Areas (SEAs) are located near the Project site. The San Gabriel Canyon SEA is located approximately 0.35-mile northwest of the Project site. The East San Gabriel Valley SEA, which includes South Hills Park and surrounding undeveloped lands within the City, is located approximately two miles southeast of the Project site.

3.5 Watersheds and Hydrology
The Project site is located within the Upper San Gabriel Hydrologic Area of the San Gabriel River Unit (Figure 2, San Gabriel River Watershed). The Groundwater Basin Number is 4-13 (California Department of Water Resources 2016). The San Gabriel River is located approximately two miles west of the Project site and the Morris Reservoir is approximately 1.4 miles to the northwest. The river flows south coming out of the San Gabriel Mountains and Item #8. Page 507
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then turns west as it makes its way to the Pacific Ocean (San Gabriel Watershed Master Plan 2006). Three main drainages are located within the Project site, which are currently intercepted by the three flood control/debris check dam structures. However, due to accumulated sediment and lack of maintenance, these structures are not functioning to retain debris or flood flows (Figure 2).

3.6 Fire History
The most recent fire (the Colby Fire) started on January 16, 2014 and occurred within the Project area. It burned approximately 1,952 acres, of which 15 acres burned within the Project site, including nearly all of the designated open space area. The fire destroyed five homes and damaged 17 structures in and around the Cities of Glendora and Azusa and the Angeles National Forest before it was contained on January 27, 2014 (CAL FIRE 2014). The Canyon Inn Fire was the last fire occurrence in the area prior to the Colby Fire and occurred 35 years prior on August 23, 1968.

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4 Methods
Data regarding biological resources present on the Project site were obtained through a review of pertinent literature and through field reconnaissance; both of which are described in detail below. The approximate 27-acre property boundary is also referred to as the Study Area within this biological resources technical report.

4.1 Literature Review
Special-status biological resources present or potentially present in the Study Area were identified through a literature search using the following sources:
▪ CDFW CNDDB (CDFW 2022a) was queried to compile a list of potentially occurring flora and fauna in the Glendora, Azusa, and surrounding seven quadrangles
▪ CNPS Inventory of Rare, Threatened, and Endangered Plants of California, 8th online edition (CNPS 2022b), was searched to compose a list of potentially occurring flora in the Glendora, Azusa, and surrounding eight quadrangles
▪ Critical Habitat online viewer (USFWS 2022a)
▪ Wetland Mapper online viewer (USFWS 2022b)
▪ Watershed Assessment, Tracking and Environmental Results (WATERS) (EPA 2017) ▪ USGS National Hydrography Dataset (USGS 2022)
▪ Historic aerials and topographic maps (Google Maps 2022; NETR 2022; USGS 2018)

4.2 Resource Mapping
Biological fieldwork for the Project was originally conducted in May and July of 2014. Given the lapse in time from the initial surveys in 2014, an updated biological assessment was requested to determine whether biological resources on site have altered since the previous survey efforts were conducted. As such, an additional biological reconnaissance survey was conducted in April 2018 to update existing biological conditions within the Study Area.

The initial rare plant survey in 2014 was conducted during a significant drought that may have limited some species’ seeds from germinating and blooming. The above average rainfall in 2019 made conditions more amenable for blooming for the rare plant species that have been recorded in the Project vicinity. Additionally, the above average rainfall in the 2016-2017 and 2018-2019 rain seasons may have altered the drainage features that were mapped in 2014, so an update to the jurisdictional waters delineation was conducted. The 2014, 2018 and 2019 biological surveys included documenting vegetation communities and land covers present within the approximate 27-acre property boundary, including the approximate 11 acres zoned for single-family residences and 16 acres zoned for open space, delineation of jurisdictional wetlands or waters, and an evaluation of the potential for special-status plant and wildlife species to occur within the 27-acre property boundary. An additional survey was conducted in January 2022 to update the existing conditions since over two years had elapsed since the previous surveys.

Table 3, Survey Dates and Conditions, lists the dates, conditions, and survey focus for each survey.

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Table 3. Survey Dates and Conditions
Date Hours Survey Focus Conditions Personnel*
5/12/2014 0815-
1615
Habitat Assessment
Special-Status Plant Survey (1st pass)
Vegetation Mapping
68˚-90˚F, 0-10% cloud
cover, 1–2 mph wind

BAS, JCP
7/22/2014 0730-
1600
Special-Status Plant Survey (2nd pass)
Jurisdictional Delineation
67˚-93˚F, clear skies,
1–2 mph wind

HLM, JCP
4/20/2018 0920-
1320
Biological Reconnaissance-level
Survey
60˚-73˚F, overcast-0%
cloud cover, 1–4 mph
wind

JCP, TKP
5/13/2019 1000-
1700
Habitat Assessment
Special-Status Plant Survey (1st pass)
Vegetation Mapping
67˚-77˚F, overcast-0%
cloud cover, 0–1 mph
wind
MC
5/15/2019 0800-
1030
California Gnatcatcher Protocol Survey 58°F-62°F, clear skies, 0-1 mph wind
TM
5/22/2019 0800-
1045
California Gnatcatcher Protocol Survey 55°F-58°F, clear skies, 0-2 mph wind
TM
5/29/2019 0900-
1100
California Gnatcatcher Protocol Survey 60°F-62°F, clear skies, 0-1 mph wind
TM
6/11/2019 0830-
1030
California Gnatcatcher Protocol Survey 68°F-75°F, clear skies, 1-2 mph wind
TM
6/21/2019 0900-
1100
California Gnatcatcher Protocol Survey 70°F-75°F, clear skies, 0-1 mph wind
MB
6/28/2019 0845-
1030
California Gnatcatcher Protocol Survey 68°F-72°F, clear skies, 1-2 mph wind
MB
7/18/2019 1000-
1700
Special-Status Plant Survey (2nd pass)
Jurisdictional Delineation
72°F-92°F, clear skies,
1-2 mph wind
MC
1/21/2022 1001-
1046
Biological Reconnaissance-level
Survey
59°F-63°F, clear skies,
0-4 mph wind
MC
Notes: Conditions: °F = degrees Fahrenheit; mph = miles per hour; Personnel: BAS = Britney A. Strittmater, HLM = Heather L. Moine, JCP = Johanna C. Page, TKP = Tracy K. Park; MC = Michael Cady; TM = Tommy Molioo; MB = Melissa Blundell

4.2.1 Vegetation Community and Land Cover Mapping
Vegetation communities on the property were mapped using the List of Vegetation Alliances and Associations (Natural Communities List; CDFW 2022b), which is based on the Manual of California Vegetation, Second Edition (MCV2; Sawyer et al. 2009). As shown in Table 2, the vegetation mapping efforts were initially conducted in May 2014 by Dudek biologists Johanna Page and Britney Strittmater. The vegetation mapping was updated in April 2018 by Dudek biologists Johanna Page and Tracy Park to record any changes to vegetation communities since the 2014 surveys (Table 3). Dudek biologist Michael Cady updated the vegetation mapping in May 13, 2019, and confirmed existing conditions in January 21, 2022.

Vegetation communities were mapped in the field directly onto a 200-scale (1 inch = 200 feet) aerial map of the property. Community classifications were selected based on site factors, descriptions, distribution, and characteristic species present within an area. Information such as dominant species and their associated cover, Item #8. Page 511
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aspect, and visible disturbance factors were recorded. To create the vegetation community map, Dudek Geographic Information Systems (GIS) technicians digitized the delineated vegetation boundaries from field maps using ArcGIS software. Holland (1986) was consulted as a resource for constituent plant species but was not used for mapping.

4.2.2 Flora and Fauna
All plant species encountered during the field surveys were identified and recorded. Latin and common names for plant species with a California Rare Plant Rank (formerly CNPS List) follow the California Native Plant Society OnLine Inventory of Rare, Threatened, and Endangered Plants of California (CNPS 2022b). For plant species without a California Rare Plant Rank, Latin names follow the Jepson Interchange List of Currently Accepted Names of Native and Naturalized Plants of California (Jepson Flora Project 2022), and common names follow the USDA NRCS PLANTS Database (USDA NRCS 2022b). A cumulative list of plant species observed on the Project site is presented in Appendix B.

Wildlife species detected during the initial field surveys by sight, calls, tracks, scat, or other signs were recorded.

Binoculars (10 x 42 magnifications) were used to aid in the identification of observed wildlife. In addition to species actually detected, expected wildlife use of the site was determined by known habitat preferences of local species and knowledge of their relative distributions in the area. Society for the Study of Amphibians and Reptiles (2017) for reptiles and amphibians, American Ornithologists Society (2019) for birds, Wilson and Reeder (2005) for mammals, and Moyle (2002) for fish. A list of wildlife species observed within the Project site is presented in Appendix C.

4.2.3 Focused Special-Status Plant Survey
Dudek Senior Biologist Michael Cady conducted focused surveys for rare and/or special-status plant species with a potential to occur within the Study Area in 2019. Two surveys were conducted, one in the spring and one in the summer, in order to cover the blooming period of the target species. Prior to the start of focused surveys, nearby reference populations were checked to verify that target species were in bloom.

The Study Area was surveyed with meandering transects searching for federally and/or state-listed plants known to occur or with the potential to occur within the Study Area. The surveys conformed to CNPS Botanical Survey Guidelines (CNPS 2001); Protocols for Surveying and Evaluating Impacts to Special Status Native Plant Populations and Natural Communities (CDFW 2018); and Guidelines for Conducting and Reporting Botanical Inventories for Federally Listed, Proposed, and Candidate Plants (USFWS 1996). All plant species encountered during the field surveys were identified to subspecies or variety, if applicable, to determine sensitivity status. Moreover, all plant species encountered in the field were recorded. If target species were encountered, data points were mapped in the field using a GPS unit.

4.2.4 California Gnatcatcher Protocol Surveys
The presence/absence focused survey for coastal California gnatcatcher (CAGN) (Polioptila californica californica) was conducted for the Project between May 15 and June 28, 2019. The survey was conducted within weather conditions and time frames appropriate for the detection of gnatcatchers. Weather conditions and survey dates are provided in Table 3. The survey routes focused on moderate to high quality habitat that dominates most of the study area. No portions of the survey routes encroached into USFWS designated critical habitat for the species.

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The survey was conducted following the currently accepted protocol of the USFWS, Coastal California Gnatcatcher (Polioptila californica californica) Presence/Absence Survey Protocol (USFWS 1997). The Project site does not occur within an approved Natural Community Conservations Plan (NCCP) area, and therefore six surveys were conducted at a minimum of 7-day intervals during the breeding season (March 15 through June 30). In accordance with the protocol, no more than 80 acres of suitable habitat were surveyed by a single permitted biologist during each site visit conducted. Survey routes completely covered all areas of suitable CAGN habitat within the survey area and allowed for complete audible and visual coverage of all suitable CAGN habitat on site.

A 200-scale topographic map (1 inch = 200 feet) overlain with vegetation polygons and the survey area was utilized during the survey. Additionally, digital mobile maps were utilized during the surveys to assist in navigating each survey area. Appropriate binoculars (e.g., 8x42 through 10x50 magnification) were used to aid in detecting and identifying bird species. A recording of gnatcatcher vocalizations was played approximately every 50–100 feet to induce responses from potentially present gnatcatchers. Vocalization-playback would have been terminated immediately upon detection of any gnatcatchers to minimize the potential for harassment.

4.2.5 Jurisdictional Delineation
A formal (routine) jurisdictional delineation of features within the Study Area was first conducted by Dudek biologists Heather L. Moine and Johanna C. Page on July 22, 2014. The Study Area was surveyed on foot for waters of the United States, including wetlands, under the jurisdiction of the USACE, pursuant to Section 404 of the federal CWA, RWQCB, pursuant to the Section 401 of the CWA and Porter-Cologne Water Quality Control Act, and under the jurisdiction of the CDFW pursuant to Section 1602 of the California Fish and Game Code. Although an additional jurisdictional delineation was not conducted for the Project in 2018, jurisdictional features were assessed for further modifications and updated accordingly during the 2018 reconnaissance-level field survey.

A second formal (routine) jurisdictional delineation was conducted for the Study Area in 2019 following the above average rainfall in 2018-2019 rain season. The survey methodology also incorporated recent CDFW determinations on the limits that the agency takes jurisdiction over. The limits of the jurisdictional waters were checked for changes during the January 2022 site visit.

Non-wetland waters of the United States are delineated based on the presence of an OHWM as determined utilizing the methodology in A Field Guide to the Identification of the Ordinary High Water Mark (OHWM) in the Arid West Region of the Western United States, A Delineation Manual (USACE 2008a). Wetland waters of the United States are delineated based on methodology described in the 1987 Corps of Engineers Wetlands Delineation Manual (USACE 1987) and the Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Arid West Region (Version 2.0) (USACE 2008b). The USACE and U.S. Environmental Protection Agency (EPA) Rapanos Guidance states that the USACE will regulate: (i) traditional navigable waters of the United States and (ii) their adjacent wetlands as well as (iii) non-navigable tributaries to traditional navigable waters that are relatively permanent and (iv) wetlands that directly about such tributaries (USACE and EPA 2008). In addition, if a significant nexus has been determined, the USACE may also assert jurisdiction over (i) non-navigable tributaries that are not relatively permanent and (ii) their adjacent wetlands, as well as (iii) wetlands that are adjacent to but that do not directly about a relatively permanent non-navigable tributary (USACE and EPA 2008).

The CDFW jurisdiction is defined to the bank of the streams/channels or to the limit of the adjacent riparian vegetation.

For shallow drainages and washes that do not support riparian vegetation, the top of bank measurement may be the same as the OHWM measurement. Areas regulated by the RWQCB are generally concurrent with the USACE, but may include features isolated from navigable waters of the U.S. that have evidence of surface water inundation.

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Features were delineated using a Trimble GeoXT handheld Global Positioning System (GPS) unit with submeter accuracy. Features were also documented directly onto a 200-scale field map (1 inch = 200 feet) with an aerial base. To assist in the determination of jurisdictional areas on site, data was collected at 59 locations (i.e., data stations). Hydrology, vegetation, and soils were assessed and data were collected and summarized. The location of data stations were collected using a Trimble GeoXT handheld GPS unit with sub-meter accuracy. Plant species were characterized as either obligate, facultative wetland, facultative, facultative upland, and/or upland per The National Wetland Plant List: 2016 Wetland Ratings (Lichvar 2016). Due to the absence of hydrophytic vegetation, soil pits were not excavated.

4.2.6 Survey Limitations
Special-status plant surveys were conducted in May and July of 2014, which resulted in detection and identification of most annual and perennial plant species that occur in the area. Additionally, all plants observed during the April 2018 vegetation mapping effort were recorded. The timing of the surveys coincided with the blooming periods for special-status plant species with a moderate to high potential to occur in the vicinity of the Project. Lower-than-average rainfall occurred in winter 2013 and 2014, which may have limited the number of plant individuals that germinated that year and limited the blooming period of those that did (WRCC 2014).

However, the above average rainfall that occurred in the winter of 2018 and 2019 provided conditions that were conducive for the detection of most plant species. A weather station at Big Dalton Dam has recorded 33.43 inches of precipitation since the beginning of the current rainy season (October 1, 2018), which is above the normal of 26.21 inches (LACDPW 2019).

Limitations of the surveys included a diurnal bias and the absence of trapping for small mammals, reptiles, and amphibians. The surveys were conducted during the daytime to maximize the detection of most animals. Birds represent the largest component of the vertebrate fauna, and because most birds are active in the daytime, diurnal surveys maximize the number of bird observations. Conversely, diurnal surveys usually result in few observations of mammals, many of which may only be active at night. In addition, many species of reptiles and amphibians are secretive in their habits and are difficult to observe using standard meandering transects. The purpose of the field surveys was to determine the likelihood of occurrence of any special-status plant or wildlife species based on the presence/absence of suitable habitat and other natural history elements that might predict their occurrence.

4.3 Special-Status Species Habitat Assessment
Endangered, rare, or threatened plant species as defined in Section 15380(b) of the CEQA Guidelines (14 CCR 15000 et seq.) are referred to as “special-status plant species” in this BRTR and include endangered or threatened plant species recognized in the context of CESA and FESA (CDFW 2019b) and plant species with a CRPR 1 through 4 (CNPS 2019b). Species with CRPR 3 or 4 may, but generally do not, qualify for protection under this provision.

Species with CRPR 3 and 4 are those that require more information to determine status and plants of limited distribution. Thus, only CRPR 3 and 4 plant species that were also locally recognized by the City of Glendora tree protection ordinance were analyzed further.

Endangered, rare, or threatened wildlife species as defined in CEQA Guidelines, Section 15380(b) (14 CCR 15000 et seq.), are referred to as “special-status wildlife species” and, as used in this report, include (1) endangered or threatened wildlife species recognized in the context of CESA and FESA (CDFW 2022c); (2) California Species of Item #8. Page 514
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Special Concern as designated by CDFW (2022d); and (3) mammals and birds that are fully protected species as described in the California Fish and Game Code, Sections 4700 and 3511.

The CNDDB and CNPS database queries conducted during the literature review resulted in a list of plant and wildlife species that have recorded occurrences within the Project vicinity. For each species evaluated, a determination was made regarding the potential for the species to occur in the Study Area based on information gathered during the field reconnaissance, including the location of the site, habitats present, current site conditions, known range, habitat associations, preferred soil substrate, life form, elevation, and blooming period.

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5 Results
This chapter describes the results of the literature review, field surveys, and habitat assessments within the Study Area. Representative site photographs of the Project site are provided in Appendix A of this BRTR.

5.1 Vegetation Communities, Land Covers,
and Floral Diversity
Six vegetation communities and land covers (including disturbed forms) were mapped in the Study Area based on general physiognomy and species composition. These vegetation communities and land cover types are described, their acreages are presented in Table 4, Vegetation Communities and Land Covers within the Study Area, and their spatial distribution are presented within Figure 4, Biological Resources.

Table 4. Vegetation Communities and Land Covers within the Study Area Vegetation Community or Land Cover
California Natural
Community Codesa
Nature-Serve
Global-State
Rarity Ranksb
Acres in
Study Area
Native Vegetation Communities
Coast Live Oak Woodland Alliance (CLOW)* 71.060.00 G5/S4 10.87 California Walnut Groves (CWG)* 72.100.00 G3/G3 1.40
Disturbed California Sagebrush Scrub
(dCSS)*

32.010.00 G5/S5 2.24
Naturalized Vegetation Communities
California Annual Non-Native Grassland
(NNG) 42.027.00 — 6.42
Non-Natural Land covers
Urban/Developed (DEV) — — 2.42
Developed-Concrete Channel (DEV-CC) — — 0.28
Disturbed Habitat (DH) — — 0.97
Parks and Ornamental Plantings (ORN) — — 2.41
Total — — 27.02
Notes: Numbers may not sum due to rounding.
a Unique codes assigned to alliances and associations.
b NatureServe Global and State rarity ranks per Faber-Langendoen et al. (2012). Natural communities with global or state ranks of 1–3 are considered Sensitive Natural Communities by CDFW (2018) and are to be addressed in the environmental review processes of CEQA.
* Special-status vegetation community per the City of Glendora (2006).

5.1.1 Coast Live Oak Woodland
Coast live oak woodland includes coast live oak as the dominant or co-dominant tree in the canopy. Coast live oak woodland has a continuous to open canopy less than 30 meters (98 feet) in height with a sparse to intermittent shrub canopy and sparse or grassy ground layer (Sawyer et al. 2009). Species associated with the coast live oak woodland alliance include bigleaf maple (Acer macrophyllum), blue oak (Quercus douglasii), box elder (Acer Item #8. Page 516
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negundo), California bay (Umbellularia californica), Engelmann oak (Quercus engelmannii), California sycamore (Platanus racemosa), California black walnut (Juglans californica), valley oak (Quercus lobata), arroyo willow (Salix lasiolepis), California black oak (Quercus kelloggii), and madrone (Arbutus menziesii) (Sawyer et al. 2009).

The coast live oak woodlands within the Study Area are located within the northern portion of the property within areas designated as open space, and along the eastern and western perimeters of the property boundary where development is proposed to occur. The coast live oak woodlands within the northern portion of the property were previously burned during the 2014 Colby fire (discussed in Section 3.8); however, the community in this portion of the site seems to be recovering well. Coast live oak woodland occurring along the eastern and western boundaries of the property remained untouched by the fire.

This community is dominated by coast live oak, though California sycamore (Platanus racemosa), southern California black walnut, and Washington fan palm (Washingtonia robusta) are also scattered throughout this vegetation community. The understory within the coast live oak woodland mapped within the eastern perimeter of the Project site and within the areas zoned as Open Space - Natural (north of the Project site) include bromes (Bromus spp.), sowthistles (Sonchus spp.), ragweeds (Ambrosia spp.), Pacific poison oak, tree tobacco (Nicotiana glauca) annual yellow sweetclover (Melilotus indicus), Cucamonga manroot (Marah macrocarpa), Bermuda buttercup (Oxalis pes-caprae), Alefeld’s pea (Lathyrus vestitus var. alefeldii), narrowleaf bedstraw (Galium angustifolium), distant phacelia (Phacelia distans), and wild canterbury bells (Phacelia minor). The understory within the coast live oak woodland mapped within the western perimeter of the Study Area is associated with nonnative and landscaped species dominated by English ivy (Hedera helix), field bindweed (Convolvulus arvensis), tree tobacco, ornamental fig trees (Ficus sp.), and smilo grass (Stipa miliacea).

The coast live oak woodland alliance is ranked by the CDFW (2018) as a G5S4 alliance. This ranking indicates that globally the alliance is widespread, abundant, and is considered secure and within California the alliance is apparently secure (CDFW 2019b). Although this alliance is not considered a special-status vegetation community by CDFW (CDFW 2022b), woodlands are recognized as a special-status vegetation community by the City of Glendora (2006).

5.1.2 California Walnut Groves
California walnut groves include California black walnut as the dominant or co-dominant tree species in the canopy.

This community has a continuous to open canopy less than 15 meters (49 feet) in height with a sparse or grassy ground layer (Sawyer et al. 2009). Species associated with California walnut groves alliance include white alder (Alnus rhombifolia), California ash (Fraxinus dipetala), toyon (Heteromeles arbutifolia), coast live oak, valley oak, arroyo willow, red willow (Salix laevigata), blue elderberry (Sambucus nigra), and California bay (Sawyer et al. 2009).

California walnut groves on site were burned during the 2014 Colby fire as discussed in Section 3.6. Many of the California walnut trees burned during the fire were observed to be re-sprouting during the 2018 site visit. Several California walnut saplings are emergent throughout canyons and hills within the northern open space portion of the property. One community dominated by California walnut groves is located within the north-central portion of the Study Area, within the designated open space area. California walnut groves on site are dominated by California black walnut and contain a grassy understory comprised of various bromes (Bromus spp.) and wild oat (Avena spp.).

Other species present include coast live oak, California sycamore (Artemisia californica), Pacific poison oak (Toxicodendron diversilobum), white sage (Salvia apiana), and black mustard (Brassica nigra).

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The California walnut grove alliance has a rank of G3S3 in CDFW (2018), meaning that it is vulnerable to extirpation or extinction both globally and within the state; and is therefore a special-status vegetation community and a high priority for inventory according to CDFW (2022b). Additionally, woodlands are recognized as a special-status vegetation community by the City of Glendora (2006).

5.1.3 Disturbed California Sagebrush Scrub
California sagebrush scrub is a community dominated or co-dominated by California sagebrush (Artemisia californica) with a continuous or intermittent shrub canopy less than two meters (seven feet) in height with a variable ground layer (Sawyer et al. 2009). This native plant community characterized by a variety of soft, low, aromatic, drought-deciduous shrubs, such as California sagebrush (Artemisia californica), coyote bush (Baccharis pilularis), Eastern Mojave buckwheat (Eriogonum fasciculatum), brittlebush (Encelia farinosa), chaparral yucca (Hesperoyucca whipplei), coastal pricklypear (Opuntia littoralis), and sages (Salvia spp.), with scattered evergreen shrubs, including lemonadeberry (Rhus integrifolia), laurel sumac (Malosma laurina), and toyon. It typically develops on steep, southfacing slopes and at times, though rarely, occurs on flooded low-gradient deposits along streams in which are scattered willows (Salix spp.) and mulefat (Baccharis salicifolia), depending on the site conditions.

This community was burned during the 2014 Colby fire, discussed further in Section 2.7. Within the Study Area, this community contains a high cover of non-native species including bromes, wild oat, castorbean (Ricinus communis), and black mustard as a result of the Colby fire. Emergent California sagebrush species including California sagebrush, laurel sumac, white sage, and common deerweed have become reestablished. Sprouting of coastal sage scrub habitats within inland areas is dependent almost entirely upon seed germination, whereas most sage scrub species re-sprout from below ground root crowns in coastal areas. Therefore, coastal sage scrub assemblages that regenerate primarily by seeding may be more vulnerable to the effects of non-natives compared with stands that regenerate by sprouting (O’Leary 1990a, 1990b). Essentially, it may take a number of years before this habitat type will reestablish, especially given the drought years preceding and following the 2014 Colby fire.

This community previously dominated hillsides throughout the northern open space portion of the Study Area; however, California sagebrush scrub is now limited approximately 1.6 acres, occurring as patches along extremely steep slopes.

California sagebrush scrub alliance has a rank of G5S5 (Faber-Langendoen et al. 2012), meaning it is globally secure and secure in the state. Although this alliance is not considered a special-status vegetation community by CDFW (2022b), coastal sage scrub habitats are recognized as a special-status vegetation community by the City of Glendora (2006).

5.1.4 California Annual (Non-Native) Grassland
California annual grassland (also referred to as non-native grassland in this report) is characterized by a mixture of weedy, introduced annuals, primarily grasses (Sawyer et al. 2009; Holland 1986). California annual grassland typically includes wild oats, bromes, black mustard, stork’s bill (Erodium spp.), dove weed (Croton setiger), Russian thistle (Salsola tragus), and Maltese star-thistle (Centaurea melitensis). It may occur where disturbance by maintenance (e.g., mowing, scraping, disking, and spraying), grazing, repetitive fire, agriculture, or other mechanical disruption has altered soils and removed native seed sources from areas formerly supporting native vegetation (Holland 1986).

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California annual grassland is located throughout the central portion of the Study Area (within northern portion of where the Project development is proposed), as well as within the northern portion of the property within areas zoned as Open Space - Natural. This vegetation community is dominated by bromes (Bromus spp.), wild oat (Avena fatua), black mustard, castorbean, redstem stork’s bill (Erodium cicutarium), Cucamonga manroot (Marah macrocarpa), and dove weed (Croton setiger). Other native species found within the eastern portion of this grassland community include sugar sumac (Rhus ovata) and hollyleaf cherry (Prunus ilicifolia ssp. ilicifolia). This area appears to have been heavily altered by regular discing activities. Tree removal activities have also occurred in this area based on past aerial maps of the area. California annual grassland also dominates slopes and ridgelines throughout the northern portion of the Study Area, within the designated open space. Following the 2014 Colby fire (discussed in Section 3.6), California annual grassland has re-vegetated hillsides previously dominated by coastal sage scrub communities. A low cover of trees and shrubs remain emergent; however, these hillsides are dominated by bromes, as well as weedy, introduced annuals such as redstem stork’s bill, prickly Russian thistle, and shortpod mustard (Hirschfeldia incana). Other native species found scattered within this grassland community include laurel sumac, California sagebrush, brittlebush, and California four o’clock (Mirabilis laevis var. crassifolia).

The California annual (non-native) grassland alliance has a rank of G4S4 (Faber-Langendoen et al. 2012), meaning that it is apparently secure both globally and within the state, and is therefore not a special-status vegetation community according to CDFW (2019b). Additionally, California annual grassland is not recognized as a specialstatus vegetation community by the City of Glendora (City of Glendora 2006a).

5.1.5 Urban/Developed
Developed land refers to areas supporting by man-made structures including homes, yards, roadways, sidewalks, and other highly modified lands supporting structures associated with dwellings or other permanent structures.

Vegetation in these areas, if present at all, is typically associated with development landscaping. Within the Study Area, developed land is limited to the southwestern portion of the proposed development, consisting of an existing private resident and associated landscaping.

Developed land is not included in the Natural Communities List (CDFW 2022b). This community is not considered a special-status vegetation community by CDFW or the City of Glendora (City of Glendora 2006a).

5.1.6 Developed-Concrete Channel
Developed-concrete channel is characterized by barren or sparsely vegetated concrete-lined channels. On site, this land cover type is largely unvegetated and conveys run-off from adjacent hillside areas into a storm drain inlet near the intersection of Palm Drive and Grand Avenue immediately south of the project site. One concrete channel was mapped within the eastern portion of the property. The concrete channel on-site is ephemeral supporting little, if any, vegetation. The channel was approximately 4 to 5 feet wide along the channel bottom and between 3 and 4 feet tall.

Developed-concrete channel is not included in the Natural Communities List (CDFW 2022b). This community is not considered a special-status vegetation community by CDFW or the City of Glendora (City of Glendora 2006a).

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5.1.7 Disturbed Land
Disturbed land includes areas that experience or have experienced high levels of human disturbance and as a result are generally lacking vegetation. Areas mapped as disturbed land may include unpaved roads, trails, and graded areas. Vegetation in these areas, if present at all, is usually sparse and dominated by non-native weedy herbaceous species. Within the study area, disturbed land includes dirt roads, and bare, open areas with less than 5% vegetative cover. Disturbed land is found throughout the proposed development area. Disturbed land is minimal within the areas designated for open space and includes a portion of a dirt road.

Disturbed land is not included in the Natural Communities List (CDFW 2022b). This community is not considered a special-status vegetation community by CDFW or the City of Glendora (City of Glendora 2006a).

5.1.8 Special-Status Vegetation Communities
During the vegetation mapping, three vegetation communities were mapped in the Study Area that are considered sensitive under CEQA by CDFW (2019b) and/or the City of Glendora (2006): California walnut groves, disturbed coastal sage scrub, and coast live oak woodlands.

Table 4 provides the acreage of each mapped vegetation community or land cover. Figure 4 shows the distribution of vegetation communities and land covers mapped within the Study Area.

5.2 Floral Diversity
A total of 129 plant species were recorded in the Study Area during 2014, 2018, 2019, and 2022 surveys, including 64 native species (50%) and 65 non-native species (50%). The cumulative list of plant species observed in the Study Area is provided in Appendix B.

5.3 Faunal Diversity
A total of 49 wildlife species were recorded in the Study Area during 2014, 2018, 2019, and 2022 surveys including 48 native species (98%) and one non-native species (2%). A full list of wildlife species observed in the Study Area is provided in Appendix C.

5.3.1 Amphibians and Reptiles
No amphibian species were observed during surveys; however, black-bellied slender salamander (Batrachoseps nigriventris) and garden slender salamander (Batrachoseps major major) have the potential to occur. Two reptile species have been observed within the Study Area, Great Basin fence lizard (Sceloporus occidentalis longipes) and California striped racer (Coluber lateralis lateralis). Additional species that are likely to occur within the Study Area include gopher snake (Pituophis catenifer annectens) and southern Pacific rattlesnake (Crotalus oreganus helleri).

5.3.2 Birds
Thirty-seven (37) bird species were observed or heard within the Study Area. Most bird species observed are common, disturbance-adapted species typical of urban and suburban settings such as house finch (Carpodacus Item #8. Page 520
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mexicanus), mourning dove (Zenaida macroura), northern mockingbird (Mimus polyglottos), acorn woodpecker (Melanerpes formicivorus), and European starling (Sturnus vulgaris). One Cooper’s hawk (Accipiter cooperii) was observed within the coast live oak woodland habitat along the western perimeter of the property. A red-tailed hawk (Buteo jamaicensis) was audibly detected north of the property during the site visit conducted in July 2014 and visually detected soaring over the Project site during the site visit conduced in April 2018. A red-shouldered hawk (Buteo lineatus) was heard calling from the ornamental vegetation in the south of the Study Area in 2019.

5.3.3 Mammals
Four mammal species were detected in the Study Area during the surveys: coyote (Canis latrans), western gray squirrel (Sciurus griseus), California ground squirrel (Spermophilus [Otospermophilus] beecheyi), and mule deer (Odocoileus hemionus). Other common species that are likely to occur include common raccoon (Procyon lotor), striped skunk (Mephitis mephitis), and Virginia opossum (Didelphis virginica).

5.4 Special-Status Biological Resources

5.4.1 Special-Status Plant Species
No special-status plant species were documented in previous surveys of the Study Area. No special-status plants species were observed during Dudek’s 2014 and 2019 focused plant surveys, which were conducted during the blooming period and under conditions that would have allowed identification for species potentially present. Therefore, no special-status plant species were determined to have a moderate or high potential to occur in the Study Area.

Appendix D, Special-Status Plant Species with Recorded Occurrences in the Project Vicinity and Their Potential to Occur in the Study Area, lists the special-status plants with potential to occur at the Project site. Species that are either not expected to occur or have a low potential to occur are identified in Appendix D and are not analyzed further in this BRTR, with the exception of thread-leaved brodiaea (Brodiaea filifolia), since it is a federally and State-listed species with local records.

Thread-Leaved Brodiaea
Thread-leaved brodiaea is federally listed as threatened and State-listed as endangered. Critical habitat for the species has been designated approximately 1.4 miles east of the Study Area (USFWS 2022a). The species is a member of the brodiaea family (Themidaceae) and is a perennial bulbiferous herb. It produces several linear leaves from an underground corm, and blue to red-purple flowers on a leafless stalk. Thread-leaved brodiaea is usually found in herbaceous plant communities such as valley needlegrass grassland, valley sacaton grassland, nonnative grassland, alkali playa, southern interior basalt vernal pools, San Diego mesa hardpan vernal pools, and San Diego mesa claypan vernal pools in association with coastal sage scrub in some locations (USFWS 2009).

These herbaceous communities occur in open areas on clay soils, soil with clay subsurface, or clay lenses within loamy, silty loam, loamy sand, silty deposits with cobbles or alkaline soils. These soil and habitat conditions do not occur in the Study Area, so thread-leaved brodiaea is not expected to occur on site. Additionally, the reference population for the species along Colby Trail, approximately 1.5 miles to the east of the Study Area, was confirmed to be in bloom during the focused rare plant survey conducted in May 2019, and the species was not observed in the Study Area.

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5.4.2 Special-Status Wildlife Species
One special-status wildlife species, yellow warbler (Setophaga petechia), was observed during the surveys in the Study Area. Three species has a moderate potential to occur in the Study Area: Southern California legless lizard (Anniella stebbinsi), coastal whiptail (Aspidoscelis tigris stejnegeri), and hoary bat (Lasiurus cinereus). Table 5, Special-Status Wildlife Species Present or with Moderate or High Potential to Occur within the Study Area, summarizes the species that occur or have a moderate or high potential to occur. Species that are either not expected to occur or have a low potential to occur are indicated in Appendix E, Special-Status Wildlife Species with Recorded Occurrences in the Project Vicinity and Their Potential to Occur in the Study Area, and are not analyzed further in this BRTR, with the exception of CAGN, since focused surveys were conducted for the species.

Table 5. Special-Status Wildlife Species Present or with Moderate or High Potential to Occur within the Study Area
Scientific
Name
Common
Name
Status
(Federal/
State) Habitat Potential to Occur
Reptiles
Anniella
stebbinsi
Southern
California
legless lizard
None/SSC Coastal dunes, stabilized
dunes, beaches, dry
washes, valley–foothill,
chaparral, and scrubs;
pine, oak, and riparian
woodlands; associated
with sparse vegetation
and moist sandy or loose,
loamy soils
Moderate potential to
occur. This species could
occur within the coast live
oak woodland, California
walnut groves, and coastal
sagebrush scrub habitats
within the Study Area.

Aspidoscelis
tigris stejnegeri
coastal whiptail None/SSC Hot and dry areas with
sparse foliage, including
chaparral, woodland, and
riparian areas
Moderate potential to
occur. This species could
occur within the coast live
oak woodland, California
walnut groves, and coastal
sagebrush scrub habitats
within the Study Area.

Birds
Setophaga
petechia
(nesting)
yellow warbler None/SSC Riparian plant
associations in close
proximity to water;
frequently found nesting
and foraging in willow
shrubs and thickets, and
in other riparian plants
including cottonwoods,
sycamores, ash, and
alders
Present. Observed during
the 2018 surveys in the
Study Area; however, the
species is not expected to
nest on site due to the lack
of riparian habitat.

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Table 5. Special-Status Wildlife Species Present or with Moderate or High Potential to Occur within the Study Area
Scientific
Name
Common
Name
Status
(Federal/
State) Habitat Potential to Occur
Mammals
Lasiurus
cinereus
hoary bat None/None Forest, woodland riparian,
and wetland habitats; also
juniper scrub, riparian
forest, and desert scrub in
arid areas; generally
roosts in dense foliage of
medium to large trees;
preferred sites are hidden
from above, with few
branches below, and have
ground cover of low
reflectivity; females and
young tend to roost at
higher sites in trees
Moderate potential to
occur. Suitable associated
day/night roosting,
maternity roosts, and
foraging habitat for the
individuals of the species
occurs within the Study
Area, and there are records
of the species from the San
Gabriel Mountains.

Puma concolor cougar None/None Scrubs, chaparral,
riparian, woodland, and
forest; rests in rocky areas
and on cliffs and ledges
that provide cover; most
abundant in riparian areas
and brushy stages of most
habitats throughout
California, except deserts
High potential to occur in
the study area as a
transient. The species is
expected to occur in the
Study Area, specifically the
hills southeast of the
project site, as a transient
during foraging, movement
through its home range, or
during the dispersal of
young; however, the fences
around the property would
limit it use by the species.

Natal dens of the species
are not expected since
females typically avoid
areas of human activity
(Center for Biological
Diversity and the Mountain
Lion Foundation 2019).

Coastal California Gnatcatcher
CAGN is a small songbird that is federally listed as threatened and a CDFW SSC species. This species is a year-round resident found below 2,500 feet in elevation within Southern California. This subspecies occurs from northwest Baja California, Mexico to Ventura County. The highest densities for CAGN occur in coastal areas of Orange and San Diego Counties (Mock 2004), with small, now disjunct populations documented for Ventura and Los Angeles Counties (Atwood et al. 1998). CAGN generally prefer open sage scrub habitats with California sagebrush as a dominant or codominant species. Nest placement is typically in areas with less than 40% slope gradient (Mock 2004).

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No CAGN (i.e., individuals and/or nests) were detected within the Study Area during any of the surveys, including the protocol surveys conducted in 2019 (see Appendix F, 2019 Focused California Gnatcatcher Survey 45-Day Report for the Silent Ranch Hillside Subdivision Project, City of Glendora, California). Therefore, the Study Area is currently considered absent of the species. This species generally has a low potential to occur within the limited coastal scrub habitat in the Study Area. The burned coastal sagebrush scrub formerly dominating the northern portion of the Study Area is now mainly re-vegetated with non-native grasslands, with only remnant patches of coastal scrub present in the northeastern corner and central portion of the Study Area.

The closest documented occurrence of this species is 3.1 miles southeast of the Study Area, approximately 0.3- mile northeast of the intersection of E. Foothill Boulevard and S. Amelia Avenue, north of San Dimas Canyon, as shown in Figure 5, Coastal California Gnatcatcher. The potential for CAGN to occur within the Study Area prior to the burn is thought to be low based on the small, disjunct populations known to occur within Los Angeles and Ventura Counties (Atwood et al. 1998; Atwood and Bontrager 2001), the terrain within the Study Area is steeper than typically preferred by this species, and there is a poor connection to existing known populations.

Mountain Lion
Pursuant to the provisions of Section 2074.2 of the Fish and Game Code, the California Fish and Game Commission (“Commission”), at its April 15-16, 2020 meeting, accepted for consideration the petition submitted to list an evolutionarily significant unit (ESU) of mountain lion (Puma concolor) in southern and central coastal California as threatened or endangered under CESA. As such, the Southern California/Central Coast ESU mountain lion population is given the protection of a listed species until its listing is permanently confirmed or denied. The species requires large areas of relatively undisturbed habitats with adequate connectivity to allow for dispersal and gene flow. Mountain lion have large home ranges that include heterogenous habitats. In the United States these often consist of pine forests, riparian and oak woodlands, streams, chaparral, and grasslands, though they are also known to occur in desert habitats (Center for Biological Diversity and the Mountain Lion Foundation 2019). Nocturnal patterns of movement and stasis suggest that mountain lions generally avoid areas with human disturbance (i.e., residential developments and two-lane paved roads) and use a variety of habitats to stalk and pursue their prey (Center for Biological Diversity and the Mountain Lion Foundation 2019). Studies have shown that when traveling or hunting, the species preferred canyon bottoms and gentle slopes and used steeper slopes and ridgelines to a lesser extent (Center for Biological Diversity and the Mountain Lion Foundation 2019). Females keep their young in dens located in rocky terrain or in dense vegetation that provide cover, but avoid roads and stay at a distance from human disturbance four times greater (approximately 600 meters) than non-reproductive mountain lions (Center for Biological Diversity and the Mountain Lion Foundation 2019) Mountain lion are expected to use the study area for foraging, movement through its home range, or during the dispersal of young, with most movement occurring at night. Natal dens are not expected since the study area sustains a relatively high level of human activities due to the adjacent residential properties.

5.5 Critical Habitat
There is no USFWS-designated critical habitat within the Study Area. There is critical habitat for CAGN approximately 4.8 miles southeast of the Study Area, southwestern willow flycatcher (Empidonax traillii extimus) critical habitat is approximately 0.9 miles northwest of the Study Area., and thread-leaved brodiaea critical habitat is approximately 1.4 miles east of the Study Area (USFWS 2022a).

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5.6 Wildlife Corridors and Habitat Linkages
Wildlife corridors are linear features that connect large patches of natural open space and provide avenues for dispersal or migration of animals and dispersal of plants (e.g., through wildlife vectors). Wildlife corridors contribute to population viability by assuring continual exchange of genes between populations, which helps maintain genetic diversity; providing access to adjacent habitat areas representing additional territory for foraging and mating; allowing for a greater carrying capacity; and providing routes for colonization of habitat lands following local population extinctions or habitat recovery from ecological catastrophes (i.e., the rescue effect).

Habitat linkages are small patches that join larger blocks of habitat and help reduce the adverse effects of habitat fragmentation. They serve as connections between habitat patches and help reduce the adverse effects of habitat fragmentation. Although individual animals may not move through a habitat linkage, the linkage is a potential route for gene flow and long-term dispersal. Habitat linkages may serve as both habitat and avenues of gene flow for small animals such as reptiles, amphibians, and rodents. Habitat linkages may be represented by continuous patches of habitat or by nearby habitat “islands” that function as steppingstones for dispersal and movement (especially for birds and flying insects). Wildlife corridors and habitat linkages provide avenues for dispersal or migration of animals that also contribute to population viability in several ways, including (1) ensuring continual exchange of genes between populations to aid in maintaining genetic diversity, (2) providing habitat for some species, (3) providing access to adjacent habitat areas representing additional territory for foraging and mating, (4) allowing for a greater carrying capacity, and (5) providing routes for colonization of habitat lands following local population extinctions or habitat recovery from ecological catastrophes.

The Study Area does not reside within any designated wildlife corridors and/or habitat linkages identified in the South Coast Missing Linkages analysis project (South Coast Wildlands 2008) or California Essential Habitat Connectivity project (Spencer et al. 2010). Although the Study Area is not located within a designated wildlife corridor or habitat linkage, the northern portion of the property contains drainage and oak woodland habitat that likely facilitates local wildlife movement. Mule deer were observed on the property during the field surveys, and are likely to use the hillsides, drainages and canyons on-site for wildlife movement. The site is also likely to support local movement of more common urban adapted species including coyote, striped skunk, and raccoon. On occasion, the canyons and drainages within the northern portion of the property may also facilitate movement for American black bear (Ursus americanus) and bobcat (Lynx rufus). However, the southern portion of the Project site and areas south and west of the Project site are dominated by residential development; and thus, is less likely to support wildlife movement. In summary, while there is potential for local wildlife movement to occur along the streambeds, canyons, ridgelines and hillsides within the northern portion of the Study Area, there is less suitable habitat for wildlife movement along the southern portion of the property where the majority of Project development is proposed.

5.7 Jurisdictional Delineation
With respect to USACE-jurisdictional waters of the U.S., including wetlands, the USACE makes the jurisdictional determination. The USACE issues two types of jurisdictional determinations—preliminary and approved.1 Both 1 The USACE issues two types of JDs—preliminary and approved. A preliminary JD is an expedited process typically initiated at the time that a 404 permit is requested for impacts to federal jurisdictional waters; the preliminary JD is non-binding and does not involve USACE review. This process is used when the permittee does not wish to request a determination that some or all of the potentially jurisdictional waters on the Project site are isolated (under the Rapanos decision) or otherwise not subject to federal jurisdiction. An approved JD is requested through submittal of a JD report and the accompanying form. It requires USACE review of the report and application of the criteria used to request a non-federal JD.

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types of determinations require a submittal of a formal jurisdiction delineation report. CDFW and RWQCB also may request a site visit to review the jurisdictional delineation and may potentially change the limits of delineation. Therefore, the jurisdiction determinations provided in this technical report are preliminary and only identify the potential for jurisdictional areas to be affected by the Project in accordance with the CEQA thresholds.

There are three main drainages within the Study Area and several swale/erosional features. One of the drainages (Drainage E) flows into a concrete channel and is located in the southeastern portions of the site. Each channel segment has been labeled with a letter (A-E) and is shown on Figure 5, Potential Jurisdictional Waters. A total of 59 data stations were recorded. Detailed notes including the OHWM (if present), feature name, general area, feature notes, dominant plant species, hydrology notes, and photographs of the data stations and associated drainages for each data station are provided in Appendix G, Jurisdictional Delineation Data.

Each drainage is described in more detail in the remainder of this section.

Drainage A
Drainage A is ephemeral and flows northwest to southeast. Data stations 01-08 were collected for this feature.

Within the northern extent of Drainage A, a natural spring is present with surface water and a small amount of water flow. No hydrophytic vegetation was observed within the natural spring. Downstream of the natural spring, the OHWM is well defined with scouring, exposed roots, and drift deposits. Drainage A does not support hydrophytic vegetation in or adjacent to the channel.

Within the downstream portion of this feature is an approximately 20-foot tall concrete weir filled with rocks and mesh wiring. A USFS placard on the weir notes “1970 Los Angeles Flood Control District”. The function at this structure is to reduce the erosion of the stream bed thus conserving soil and water and encouraging plant growth.

It was constructed in cooperation with the United States Forest Service. For your safety please stay off." The OHWM end just downstream of the weir, making Drainage A an isolated feature.

Due to the absence of hydric soils and hydrophytic vegetation, there are no wetlands present within Drainage A.

However, Drainage A exhibits evidence of surface flow and the OHWM varies between 2-26 feet with OHWM indicators consisting of absence of vegetation, sediment deposition, and shelving. The feature is mostly vegetated with scattered shrubs, forbs, and non-native grasses, within an overstory canopy from coast live oak woodland.

Additional information recorded for Drainage A is provided in Appendix G.

Drainages B, C, and D
Drainages B, C and D are ephemeral drainages within the north-central portion of the site. Drainages B and C are tributaries to Drainage D. Drainage D generally flows north to the south. Data stations 09-25 were collected for these three features. All three drainages have steep slopes and lack hydrophytic vegetation within the OHWM or adjacent to the channel. The features are vegetated with a dense understory dominated by poison oak, edible fig, blue elderberry, and non-native grasses. The uppermost portions of Drainage C and D are within California walnut groves and the remainder is within coast live oak woodlands.

Due to the absence of hydric soils and hydrophytic vegetation, there are no wetlands present within Drainages B, C or D, but they do exhibit evidence of surface flow and the OHWM varies between 1-12 feet wide. OHWM indicators consist of absence of vegetation, sediment deposition, debris deposition, exposed roots, and shelving. However, Drainages B, C, and D are isolated features, with no observable connection to downstream waters.

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Drainage E
Drainage E is ephemeral and flows north to south. The upstream portion is earthen-lined and flows into a concretelined trapezoidal channel. Data stations 42-51 were collected for the earthen-lined portion of this drainage. It is earthen-lined for approximately 7,193 linear feet and then flows are contained within a concrete-lined trapezoidal channel. Because the channel is concrete-lined, it lacks vegetation and there is no hydrophytic vegetation adjacent to the channel. No surface water was observed during the site visit. Data stations 52–57 were collected in the concrete-lined portion of Drainage E. The bottom of the concrete channel, measured as the OHWM, varies between 4 and 5 feet. The slopes of the concrete channel are between 3 and 4 feet tall.

The upstream earthen-lined portion of Drainage E is densely vegetated within a coast live oak woodland and understory dominated by black mustard, castorbean, greenspot nightshade (Solanum douglasii), and non-native grasses. The concrete channel has a disturbed California sagebrush scrub, non-native grasslands, and ornamental vegetation adjacent to the top of bank.

Due to the absence of hydric soils and hydrophytic vegetation in this portion of the channel, there are no wetlands present within Drainage E. However, the earthen-lined portion of Drainage E exhibits evidence of surface flow and the OHWM varies between 2 and 25 feet wide with OHWM indicators consisting of sediment deposition, debris deposition, exposed roots, and shelving. Drainage E flows into a storm drain inlet near the intersection of Palm Drive and Grand Avenue located immediately south of the Study Area site. It is assumed that this storm drain flows into the closest drainage, Little Dalton Wash (concrete channel), based upon the general topography of the region.

Little Dalton Wash is connected downstream to Big Dalton Wash, which is connected to the San Gabriel River.

Waters from the San Gabriel River flow into the Pacific Ocean.

5.7.1 Summary of Jurisdictional Delineation Results
Due to the absence of hydric soils and hydrophytic vegetation, there are no wetlands present within the Project site.

Evidence of flow and presence of an OHWM was documented in Drainages A–E; however, Drainages A-D are isolated linear features which are typically not waters of the U.S. but are waters of the State and CDFW jurisdictional resources.

Based upon the data gathered during the site visit, Drainages A–E may be under the jurisdiction of the USACE, RWQCB, and/or CDFW. Table 6, Potential Jurisdictional Waters within the Study Area, lists the acreage of the three potential jurisdictional waters types. It is anticipated that this BRTR would support the applications for a Section 404 Permit from the USACE, a Section 401 Water Quality Certification from the Los Angeles RWQCB, and a California Fish and Game Code Section 1602 Streambed Alteration Agreement from the CDFW.

Table 6. Potential Jurisdictional Waters within the Study Area Jurisdictional Waters Type Acres
USACE waters of the United States 0.45
RWQCB waters of the state 0.47
CDFW streambed and bank, with coast live oak woodland 2.18 CDFW streambed and bank, with non-riparian habitat* 0.36 * Parks and ornamental plantings, disturbed habitat, and developed-concrete channel Item #8. Page 527
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5.8 Regional Resource Planning
The proposed Project does not occur within any adopted Habitat Conservation Plans (HCP), NCCP, or any other approved local, regional, or state conservation plans. Trees that are protected under the City Tree Preservation Ordinance No. 1768 are found in the Study Area.

5.8.1 City of Glendora Tree Preservation Ordinance No. 1768 A tree survey for the Project was completed in February 2014 (Bennett 2014) following the Colby Fire, which burned some of the trees in the open space portion of the Study Area. A second tree survey was conducted on August 15, 2018 (Bennett 2018). A large number of the trees including native oaks were damaged by the Colby Fire have succumbed to their injuries in the four and a half years since the fire. In August 2019, the trees surveyed in 2018 were checked to determine if any other mortality occurred. In August 2020, a third and final tree survey was performed.

The results of this survey are included as Appendix H, Tree Report (peer reviewed), along with the report issued in August 2019. The below discussion includes the results of the most recent (August 2020) tree survey.

A total of 835 trees were surveyed and mapped within the Study Area. Of these 835 trees, 639 are considered protected per the City of Glendora, and are listed in Table 7, Protected Trees in the Study Area. Four native trees species were identified: California black walnut, California sycamore, coast live oak, and toyon. An additional 24 nonnative or non-natural native species (native to California but planted for ornamental landscaping) were identified in the Study Area. Approximately 85 of the trees were assessed as having poor health (see Appendix H).

Table 7. Protected Trees in the Study Area
Scientific Name Common Name Number of Trees
Native Trees
Heteromeles arbutifolia toyon 1
Juglans californica California black walnut 28
Platanus racemosa California sycamore 10
Quercus agrifolia coast live oak 398
Subtotal 437
Non-Native or Non-Natural Native Trees*
Araucaria bidwillii bunya 2
Casuarina cunninghamiana river she-oak 9
Cedrus atlantica 'glauca' blue atlas cedar 1
Cedrus deodara deodar cedar 7
Ceratonia siliqua carob 2
Citrus spp. citrus tree 3
Corymbia maculata spotted gum 4
Eucalyptus cladocalx sugar gum 4
Eucalyptus robusta swamp mahogany 3
Ficus benjamina weeping fig 2
Ficus elastica rubber tree 1
Grevillea robusta silk oak 9
Jacaranda mimosifolia jacaranda 2
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Table 7. Protected Trees in the Study Area
Scientific Name Common Name Number of Trees
Juglans regia English walnut 1
Olea europaea fruitless olive 28
Phoenix canariensis Canary Island date palm 19
Pinus canariensis Canary Island pine 28
Pinus pinea Italian Stone Pine 3
Pittosporum undulatum Victorian box 1
Pseudotsaya menziesii Douglas-fir 1
Sambucus canadensis American elderberry 1
Schinus molle Peruvian pepper 8
Schinus terebinthifolia Brazilian pepper 1
Washingtonia robusta Mexican fan palm 62
Subtotal 202
Total 639
Notes:
* Non-Natural Native Trees are species that are native to California, but the Study Area is outside the natural range of the species and are assumed to have been planted for landscaping.

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6 Project Impacts
This chapter addresses direct and indirect impacts to biological resources that would result from implementation of the proposed Project, along with the significance determinations for the proposed or potential impacts. Figure 7, Impacts to Biological Resources, illustrates the permanent and temporary impacts to biological resources in the Study Area.

6.1 Definition of Impacts
This section defines the types of impacts that would occur as are result of Project implementation, including direct permanent impacts, direct temporary impacts, and indirect impacts.

6.1.1 Direct Permanent Impacts
Direct permanent impacts refer to the absolute and permanent physical loss of a biological resource due to clearing and grading associated with implementation of the Project and are analyzed in four ways: (1) permanent loss of vegetation communities, land covers, and general wildlife and their habitat; (2) permanent loss of or harm to individuals of special-status plant and wildlife species; (3) permanent loss of suitable habitat for special-status species; and (4) permanent loss of wildlife movement and habitat connectivity in the Project area. Direct impacts associated with the proposed Project include the designed residential development and the footprint of proposed flood/debris control infrastructure (e.g., elevated storm drain inlets, debris basin, and access road).

6.1.2 Direct Temporary Impacts
Direct temporary impacts refer to a temporal loss of vegetation communities and land covers resulting from vegetation and land cover clearing and grading associated with construction of proposed temporary haul roads and construction of proposed permanent new access roads, slope remediation, grade control structures, installation of culverts, and other improvements required for the Project. The main criterion for direct temporary impacts is that impacts would occur for a short period of time and would be reversible. Areas temporarily disturbed by construction activities would be restored and revegetated with a native species mix similar to that which existed prior to disturbance following completion of work in the area such that full biological function can be restored. Direct temporary impacts associated with the proposed Project include temporary access, staging, and other work areas associated with installation of the flood/debris control infrastructure.

6.1.3 Indirect Impacts
Indirect impacts are reasonably foreseeable effects caused by Project implementation on remaining or adjacent biological resources outside the direct construction disturbance zone that may occur during construction (i.e., shortterm construction related indirect impacts) or later in time as a result of the development (i.e., long-term, or operational, indirect impacts). Indirect impacts may affect areas within the defined Project area but outside the construction disturbance zone, including open space and areas outside the Project area, such as downstream effects. Indirect impacts include short-term effects immediately related to construction activities and long-term or chronic effects related to the human occupation of developed areas (i.e., development-related long-term effects) and/or routine maintenance of infrastructure.

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For the proposed Project, it is assumed that the potential short-term indirect impacts resulting from construction activities include dust, chemical pollution, noise, and general human presence that may temporarily disrupt species and habitat vitality, as well construction-related soil erosion and runoff that could affect downstream resources. With respect to potential downstream impacts, all Project grading will be subject to the typical restrictions and requirements that address erosion and runoff, including the federal CWA, National Pollution Discharge Elimination System (NPDES), and preparation of a Storm Water Pollution Prevention Plan (SWPPP).

The project would also result in long-term indirect impacts resulting from an increase in residential developed uses and routine maintenance of flood/debris control infrastructure. Such long-term indirect impacts include potential discharges of chemical pollutants, presence of non-native, invasive plant and animal species, increased human activity, construction equipment noise, and altered fire regime.

6.1.4 Explanation of Findings of Significance
Impacts to sensitive vegetation communities or riparian habitat, special-status plant species, special-status wildlife species, wildlife corridors and habitat connectivity, and regional resource planning must be analyzed to determine whether such impacts are significant. CEQA Guidelines Section 15064(b) states that an ironclad definition of “significant” effect is not possible because the significance of an activity may vary with the setting. However, CEQA Guidelines Section 15065(a) lists impacts that are helpful in defining whether a project may have a significant effect on the environment. Mandatory findings of significance, which require preparation of an EIR, occur when there is substantial evidence that a project could: (1) substantially degrade the quality of the environment, (2) substantially reduce the habitat of a fish or wildlife species, (3) cause a fish or wildlife population to drop below self-sustaining levels, (4) threaten to eliminate a plant or animal community, or (5) reduce the number or restrict the range of a rare or endangered plant or animal.

The following are the significance thresholds for biological resources provided in the CEQA Appendix G environmental checklist, which states that a project would potentially have a significant effect if it:
▪ Impact BIO-1. Would the project have a substantial adverse effect, either directly or through habitat modifications, on any species identified as being a candidate, sensitive, or special-status species in local or regional plans, policies, or regulations, or by CDFW or USFWS? ▪ Impact BIO-2. Would the project have a substantial adverse effect on any riparian habitat or other sensitive natural community identified in local or regional plans, policies, or regulations, or by CDFW or USFWS? ▪ Impact BIO-3. Would the project have a substantial adverse effect on federally protected wetlands as defined by Section 404 of the Clean Water Act (including but not limited to marsh, vernal pool, coastal, etc.) through direct removal, filling, hydrological interruption, or other means? ▪ Impact BIO-4. Would the project interfere substantially with the movement of any native resident or migratory fish or wildlife species or with established native resident or migratory wildlife corridors, or impedes the use of native wildlife nursery sites?
▪ Impact BIO-5. Would the project conflict with any local policies or ordinances protecting biological resources, such as a tree preservation policy or ordinance? ▪ Impact BIO-6. Would the project conflict with the provisions of an adopted habitat conservation plan, natural community conservation plan, or other approved local, regional, or state habitat conservation plan? Item #8. Page 531
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The evaluation of whether or not an impact to a particular biological resource is significant must consider both the resource itself and the role of that resource in a regional context. Substantial impacts are those that contribute to, or result in, permanent loss of an important resource, such as a population of a rare plant or animal. Impacts may be important locally because they result in an adverse alteration of existing site conditions but considered not significant because they do not contribute substantially to the permanent loss of that resource regionally. The severity of an impact and the offsetting benefits of mitigation are the primary determinants of whether or not that impact can be mitigated to a less-than-significant level.

6.2 Impacts to Special-Status Species
No special-status plant species were observed during the focused surveys and none have a medium or high potential to occur. Therefore, neither direct temporary or permanent impacts, nor indirect impacts, are expected and impacts would be less than significant. No mitigation is required.

6.2.1 Impacts to Special-Status Wildlife Species
Appendix E indicates the special-status wildlife species that were detected or have high or moderate potential to occur within the Study Area. Direct impacts to special-status wildlife species were quantified by comparing the limits of the proposed Project footprint with suitable habitat for these wildlife species and are further discussed below.

6.2.1.1 Direct Impacts
Special-Status Amphibians and Reptiles
No special-status amphibians or reptiles were detected during the 2014, 2018 and 2019 field surveys. Two specialstatus reptile species have moderate potential to occur in the Study Area: Southern California legless lizard and coastal whiptail. These species are both designated as CDFW SSC. Due to the presence of suitable habitat, and/or documented occurrences for these species within the vicinity of the Project site, there is potential for these species to occur on site. If these species are determined to occur on the Project site prior to construction, Project-related impacts could be considered significant if the impact causes the greater population of either species to drop below self-sustaining levels. These species are vulnerable to mortality or injury if struck by moving vehicles or equipment if present on-site during construction. These species are also vulnerable to mortality or injury during vegetation and ground disturbing activities associated with construction because they tend to be cryptic, slow moving, and below ground or under rocks or debris during cooler periods. No direct temporary impacts would occur; however, because habitat loss and/or mortality or injury to individual species is a reasonable possibility, direct permanent impacts would be considered potentially significant.

Project implementation of MM-BIO-1 would reduce potential direct impacts special-status wildlife (Southern California legless lizard and coastal whiptail) to a less-than-significant level through pre-construction surveys, avoidance, and potential relocation.

Special-Status Birds
One special-status bird species (yellow warbler) has a moderate potential to nest and forage within the open shrublands throughout the Project site. This species is a CDFW SSC and there is a potential for this species to nest and/or forage within or immediately adjacent to the proposed development footprint. If this species is determined Item #8. Page 532
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to occur on the Project site prior to construction, Project-related direct impacts would occur particularly if construction would result in direct impacts to nesting and foraging habitat for yellow warbler.

Additionally, the trees and shrubs within the Project site provides suitable nesting habitat for bird species (i.e., yellow warbler and raptors) protected under the Migratory Bird Treaty Act (MBTA; 16 USC 703-712) and California Fish and Game Code Sections 3503.5, 3503, and 3513. Trimming, pruning, and/or removal of trees and shrubs may occur as a result of construction of the Project, and could disrupt breeding activity. There would be no direct temporary impacts; however, there may be a potential for a direct permanent impact to occur to nesting birds (i.e., direct impacts to individuals, active nests, eggs, or young), particularly during the general nesting season of February 1 through August 31. Construction activities that could result in direct impacts to nesting birds include vegetation and tree removal during grading activities. Project implementation of MM-BIO-2 (i.e., seasonal recommendations, pre-construction survey, avoidance buffers, and monitoring) would reduce potential direct impacts to a less-than-significant level.

Special-Status Mammals
No special-status mammals were detected during the 2014 and 2018 field surveys. No special- One special-status bat species (hoary bat) has a moderate potential for day/night roosting, maternity roosts, and foraging habitat within the Study Area. If this species is determined to occur on the Project site prior to construction, it is highly unlikely that short-term construction activities could cause the greater population of this special-status species to drop below self-sustaining levels due to the relatively small area of construction activity and the short-term nature of the construction schedule. No direct temporary impacts would occur; however, because habitat loss and/or mortality or injury to individual species is a reasonable possibility, direct permanent impacts would be considered potentially significant.

Project implementation of MM-BIO-3 (i.e., seasonal recommendations, pre-construction survey, avoidance buffers, and monitoring) would reduce potential direct impacts to a less-than-significant level. Direct impacts to day roosts occupied by individual special-status bat species would be less than significant as the impact would not be expected to reduce populations to below self-sustaining levels.

6.2.1.2 Indirect Impacts
Potential short-term indirect impacts to special-status wildlife could result from fugitive dust and increased human activity. Noise generated by construction activities, including vegetation removal and grading, that would be conducted during the avian breeding season (February 1 through August 31), could result in indirect impacts to nesting birds. Noise related to these activities has the potential to disrupt reproductive and feeding activities.

Nighttime construction is not expected for the Project, so indirect impacts on potentially foraging special-status bats is not expected. Potential temporary indirect impacts during construction may cause mortality due to the abandonment of an active nest and would be considered significant, absent mitigation. Project implementation of MM-BIO-2 would reduce these potential indirect impacts to a less-than-significant level. Long-term indirect impacts to special-status wildlife are not expected.

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6.3 Impacts to Vegetation Communities and Land Covers

6.3.1 Direct Impacts
Direct permanent and temporary impacts to vegetation communities and land covers within the Study Area are summarized in Table 8, Permanent and Temporary Direct Impacts to Vegetation Communities and Land Covers, and illustrated on Figure 5, Impacts to Biological Resources, Direct impacts were quantified by calculating the Project impact area, which was delineated based on engineering plans that identified the limits of grading, within the boundaries of the vegetation communities mapped in the Study Area.

Table 8. Permanent and Temporary Direct Impacts to Vegetation Communities and Land Covers
Vegetation Community/
Land Cover Type
Direct
Permanent
Impacts
(acres)
Direct
Temporary
Impacts
(acres)
Remaining within
the Property
Boundary
(acres)
Native Vegetation Communities
Coast Live Oak Woodland Alliance (CLOW)* 7.71 — 3.17
California Walnut Groves (CWG)* — 0.01 1.39
Disturbed California Sagebrush Scrub (dCSS)* 0.20 0.71 0.65 Naturalized Vegetation Communities
California Annual Non-Native Grassland (NNG) 2.02 1.47 2.93 Non-Natural Land Cover Types
Urban/Developed (DEV) 0.47 — 2.42
Developed-Concrete Channel (DEV-CC) 0.28 — —
Disturbed Habitat (DH) 0.87 0.10 —
Parks and Ornamental Plantings (ORN) 1.77 — —
Total** 13.32 2.29 10.30
Notes:
* Special-status vegetation community per CDFW and/or the City of Glendora (2006). ** Total may not sum due to rounding.

Direct impacts to vegetation communities would occur as a result of earthwork and/or vegetation removal activities.

Direct permanent impacts would occur in the areas proposed for the development of graded pads and a private street in the southern section of the Project site, and for proposed flood/debris control improvements and access road in the northern section of the Project site. Direct temporary impacts to vegetation communities and land covers would occur only within the northern section of the Project site associated with the proposed flood/debris control improvements. As part of the proposed Project design, the affected areas would be hydroseeded with native seeds to facilitate the reestablishment of vegetative cover. Additionally, container trees and shrubs will be installed in the minimal grading/grooming areas per the Project’s approved landscaping plan.

The proposed Project would have 7.91 acres of direct permanent impacts to two sensitive vegetation communities (City of Glendora 2006a): coast live oak woodland and disturbed California sagebrush scrub. The Project would have 0.72 acres of direct temporary impacts to the two sensitive vegetation communities: California walnut woodland and disturbed California sagebrush scrub. Permanent and temporary direct impacts to coast live oak Item #8. Page 534
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woodland, California walnut grove woodland, and disturbed California sagebrush scrub would be considered significant absent mitigation. Project implementation of MM-BIO-4 (i.e., preparation and implementation of a Habitat Restoration Plan) would reduce potential direct impacts to a less-than-significant level. Direct impacts to annual non-native grassland and non-natural land cover types are less than significant because these communities/land cover types are not considered sensitive by CDFW and/or the City of Glendora.

6.3.2 Indirect Impacts
Potential short-term indirect impacts to special-status vegetation communities in the Study Area would primarily result from construction activities and include impacts related to or resulting from the generation of fugitive dust, and increased human activity, the introduction of pollutants from construction equipment. Excessive dust can decrease the vigor and productivity of vegetation through effects on light, penetration, photosynthesis, respiration, transpiration, increased penetration of phytotoxic gaseous pollutants, and increased incidence of pests and diseases.

Erosion and chemical pollution (releases of fuel, oil, lubricants, paints, release agents, and other Project-related materials) may affect special-status vegetation communities. The use of chemical pollutants can decrease the number of plant pollinators, increase the existence of non-native plants, and cause damage to and destruction of native plants. These potential short-term, construction-related indirect impacts could affect the special-status vegetation communities in the Study Area.

Potential construction-related indirect impacts to special-status vegetation communities would be less than significant with the implementation of MM-BIO-5 (i.e., demarcation of disturbance limits and biological monitoring during vegetation removal).

Long-term indirect impacts to sensitive vegetation communities could result from Project implementation due activities associated with the residential development that includes chemical pollutants; non-native, invasive plant and animal species; increased human activity; and altered fire regime. Potential long-term indirect impacts to sensitive vegetation communities outside of the impact area would be significant absent mitigation. However, it is expected that the Project development will be subject to Glendora municipal codes and will have a homeowners association (HOA) that will be responsible for implementing Covenants, Conditions & Restrictions (CC&Rs) that must be reviewed by the City Attorney. It is expected that CC&Rs will contain restrictions on the use of chemicals that could pollute waters; ban the use of invasive species that are found on the California Invasive Plant Council’s (CalIPC) Inventory (Cal-IPC 2022); fencing between the development and preserved open space areas to limit human intrusion, and rules regarding fuel modification to limit the threat of fires. Therefore, long-term indirect impacts to sensitive vegetation communities would be less than significant based on compliance with regulations that would reduce the severity of potential indirect impacts such that sensitive vegetation communities would be expected to persist and have similar function to existing conditions, in areas adjacent to development.

6.4 Impacts to Jurisdictional Waters

6.4.1 Direct Impacts
The Project would result in both permanent and temporary direct impacts to jurisdictional waters during the construction the installation of the three debris basins (i.e., west, middle, and east basins) and the removal of the existing concrete channel, which occurs within the eastern portion of the property. The new debris basins and on site buried storm drain pipe system are proposed to be constructed to direct storm water flows south of the tract boundary where it will be released into the existing County Storm Drain system. Construction of the new buried Item #8. Page 535
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storm drain system will eliminate the need for the concrete channel within the southern portion of Drainage E.

Temporary direct impacts will occur due to grading activities associated with the installation of the new debris basins. Table 9, Permanent and Temporary Direct Impacts to Potential Jurisdictional Waters, includes the acres of permanent and temporary impact, which are illustrated in Figure 7, Impacts to Biological Resources.

Table 9. Direct Impacts to Potential Jurisdictional Waters Jurisdictional Waters Type
Direct Permanent
Impacts
(acres)
Direct Temporary
Impacts
(acres)
Remaining within
the Property
Boundary
(acres)
USACE waters of the United States 0.38 0.07 <0.01
RWQCB waters of the state 0.50 0.11 0.02
CDFW streambed, bank, and
riparian vegetation (coast live oak
woodland*)

2.05 — 0.44
Notes:
* Includes 1.77 acres of coast live oak woodland
There are no jurisdictional wetlands in the Study Area. The natural drainages and the concrete channel are potentially regulated by the USACE, RWQCB, and/or CDFW. The proposed Project would result in direct temporary and/or permanent impacts to these potentially jurisdictional waters, as summarized above. Direct impacts include discharge of fill (i.e., grading and construction/reconstruction of structures) to potentially jurisdictional waters, which would alter the size, scope, and character of these aquatic resources and therefore would be significant, absent mitigation.

Potential permanent and/or temporary impacts to jurisdictional waters be reduced to less than significant with the implementation of MM-BIO-5 and MM-BIO-6 (on-site restoration and/or land acquisition, mitigation program funding, and/or mitigation bank credits). Consultation with, and permit issuance from, USACE, RWQCB, and CDFW may result in higher mitigation ratios and specific criteria for restoration beyond the minimum standards presented in this mitigation.

6.4.2 Indirect Impacts
Potential temporary indirect impacts to jurisdictional waters in the Study Area would primarily result from construction activities and would include impacts from the generation of fugitive dust and the introduction of chemical pollutants (including herbicides). Excessive dust can decrease the vigor and productivity of vegetation through effects on light, penetration, photosynthesis, respiration, transpiration, increased penetration of phytotoxic gaseous pollutants, and increased incidence of pests and diseases. Erosion and chemical pollution (releases of fuel, oil, lubricants, paints, release agents, and other construction materials) may affect wetlands/jurisdictional waters.

The release of chemical pollutants can reduce the water quality downstream and degrade adjacent habitats.

However, during construction, erosion-control measures would be implemented as part of the Storm Water Pollution Prevention Plan (SWPPP) for the Project. Prior to the start of construction activities, the Contractor is required to file a Permit Registration Document (PRD) with the State Water Resources Control Board (SWRCB) in order to obtain coverage under the National Pollutant Discharge Elimination System (NPDES) General Permit for Storm Water Discharges Associated with the Construction and Land Disturbance Activities (Order No 2009-009- DWQ, NPDES No. CAS000002) or the latest approved general permit. This permit is required for earthwork that Item #8. Page 536
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result in the disturbance of one acre or more of total land area. The required SWPPP will mandate the implementation of best management practices (BMPs) to reduce or eliminate construction-related pollutants in the runoff, including sediment. Therefore, temporary indirect impacts would be less than significant based on compliance with regulations that would reduce the severity of potential short-term indirect impacts such that jurisdictional waters would be expected to persist and have similar function to existing conditions, in areas adjacent to development.

Long-term indirect impacts to jurisdictional waters could result from Project implementation due activities associated with the residential development that includes chemical pollutants; non-native, invasive plant and animal species; increased human activity; and altered fire regime. Potential long-term indirect impacts to jurisdictional waters outside of the impact area would be significant absent mitigation. However, it is expected that the Project development will be subject to Glendora municipal codes and will have an HOA that will be responsible for implementing CC&Rs that must be reviewed by the City Attorney. It is expected that CC&Rs will contain restrictions on the use of chemicals that could pollute waters; ban the use of invasive species that are found on the Cal-IPC Inventory (Cal-IPC 2019); fencing between the development and preserved open space areas to limit human intrusion, and rules regarding fuel modification to limit the threat of fires. Therefore, long-term indirect impacts to jurisdictional waters would be less than significant based on compliance with regulations that would reduce the severity of potential long-term indirect impacts such that jurisdictional waters would be expected to persist and have similar function to existing conditions, in areas adjacent to development.

6.5 Impacts to Wildlife Corridors and Habitat Connectivity The Project site does not occur within any designated wildlife corridors or habitat linkages (South Coast Wildlands 2008, Spencer et al. 2010). The canyons and drainages within the designated open space areas in the northern portion of the property may facilitate local north-south wildlife movement through the area; however, the features do not provide a connection to other large open space areas to the south that may be used by wildlife. Therefore, neither direct temporary or permanent impacts, nor indirect impacts, are expected and impacts would be less than significant. No mitigation is required.

6.6 Regional Resource Planning
The Study Area does not occur within any proposed or approved HCP or NCCP (CDFW 2019c) and is outside the Angeles National Forest boundaries (USGS 2018). Trees that are protected under the City Tree Preservation Ordinance No. 1768 would be directly and indirectly impacted due to the construction of the Project.

6.6.1 Direct Impacts
It is anticipated that 455 protected trees would be removed as part of Project construction. These direct permanent impacts would be significant and there would be no temporary impacts. Project implementation of MM-BIO-7 (i.e., tree replacement) would reduce potential direct impacts to a less-than-significant level.

6.6.2 Indirect Impacts
Indirect impacts to trees are the result of changes to the site that may cause tree decline, even when the tree is not directly injured. Site-wide changes affecting trees include diverting runoff and stormwater, creating retention Item #8. Page 537
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and detention ponds, relocating streams or making improvements to streams, lowering or raising water tables, altering the capacity for soil moisture recharge, removing vegetation, or damming underground water flow (Matheny and Clark 1998). Indirect tree impacts may potentially occur to trees that are within 25 feet of the proposed Project’s limits of grading.

Indirect impacts could potentially result in tree mortality adjacent to the Project work areas, which would be significant, absent mitigation, under the City’s Tree Ordinance. Project implementation of MM-BIO-8 (i.e., tree protection and monitoring) would reduce potential indirect impacts to a less-than-significant level.

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INTENTIONALLY LEFT BLANK
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7 Mitigation
The following mitigation measures shall be implemented during the proposed Project to reduce the significant impacts identified in Chapter 6 to a less-than-significant level.

7.1 Impact BIO-1: Special-Status Species
Significant direct and indirect impacts to special-status species can be mitigated to less than significant with implementation of the following measures:

MM-BIO-1 Special-Status Wildlife Relocation Plan. The applicant shall contract with a qualified biologist, whom shall be selected subject to the City’s approval, to prepare a Relocation Plan for Terrestrial Reptiles (Southern California legless lizard and coastal whiptail). The Plan shall at minimum include: identification of potentially occupied habitat, the timing and locations where surveys should be conducted; the habitat and conditions in the proposed relocation site(s); the methods that would be used for trapping and relocating the individual species; and requirements to provide the documentation/recordation of the species and number of animals relocated. The Plan shall be submitted to CDFW for review and must be approved by CDFW prior to commencement of any vegetation clearing or earthwork activities on the Project site.

Pre-Construction Surveys. Prior commencement of any vegetation clearing or earthwork activities on the Project site, a qualified biologist shall conduct a preconstruction survey within areas of suitable habitat identified in the Relocation Plan for Terrestrial Reptiles for specialstatus species wildlife (Southern California legless lizard and coastal whiptail). The biologist shall look for special-status species that may be located within or immediately adjacent to (within 100 feet) of the Project work areas, as permitted by access. Any individual specialstatus wildlife species observed within the Project work areas during the pre-construction survey shall be flushed and moved out of harm’s way to avoid direct impacts to these species (with special-status reptiles documented and relocated as per the approved Relocation Plan).

Monitoring. A qualified biologist shall be present during initial ground-disturbing activities within the Project site. The qualified biologist shall possess an appropriate California scientific collecting permit to handle special-status species likely to occur in the Project area. If specialstatus species reptiles are detected in the work area during the surveys, the authorized biologist will capture and relocate individuals to nearby undisturbed areas with suitable habitat outside of the construction area, but as close to their origin as possible (consistent with the approved Relocation Plan). All wildlife moved or flushed during Project activities shall be documented by the biologist and CDFW shall be notified.

MM-BIO-2 Direct and Indirect Impacts to Special-Status and Nesting Birds.

Nesting Bird Avoidance. Initiation of construction activities, including initial vegetation clearing, should avoid the migratory bird nesting season (February 1 through August 31) in order to avoid any potential significant impact to birds that may be nesting on the Project site. If construction activities must be initiated during the migratory bird-nesting season, an avian nesting survey Item #8. Page 540
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of the Project site and contiguous habitat within 500 feet of all Project-related impact areas shall be conducted for protected migratory birds and active nests. The avian nesting survey shall be performed by a qualified wildlife biologist, subject to the City’s approval, within 72 hours prior to the start of construction-related activity in accordance with the Migratory Bird Treaty Act (16 USC 703–712) and California Fish and Game Code Sections 3503, 3503.5, and 3513.

If an active bird nest is found, the nest shall be flagged and mapped on the construction plans along with an appropriate no disturbance buffer, which shall be determined by the qualified wildlife biologist based on the species’ sensitivity to disturbance (minimum of 50 feet for common, urban-adapted species, 300 feet for other passerine species, and 500 feet for raptors and special-status species). The “no disturbance buffer” area shall be demarcated in the field with flagging and stakes or construction fencing and shall be avoided until the nest is vacated and the juveniles have fledged. The qualified biologist shall have the authority to stop work on the Project site and shall serve as a construction monitor during those periods when construction activities will occur near active nest areas to ensure that no inadvertent impacts on these nests occur.

MM-BIO-3 Bat Roost Avoidance. Initiation of construction activities, including initial vegetation clearing, should avoid the maternity roosting season (March through August), in order to avoid any potential significant impact to bat maternity roosts. If construction activities must be initiated during the maternity roosting season, a roost survey must be conducted by a qualified biologist, subject to the City’s approval. The roost survey for roosting bats shall be conducted on the Project site, including all trees and structures within 300 feet of Project-related impact areas, and shall be conducted no less than 30 days prior to commencement of construction activities.

If maternity roosting is identified, those trees and/or occupied structures shall not be removed during the bat maternity roost season (March to August) and a minimum 300-foot buffer shall be established. The “no disturbance buffer” area shall be demarcated in the field with flagging and stakes and the roost shall be monitored by a qualified biologist until roost is vacated and juveniles have fledged.

7.2 Impact BIO-2: Sensitive Vegetation Communities
Significant direct and indirect impacts to sensitive vegetation communities can be mitigated to less than significant with implementation of the following measures:

MM BIO-4 Mitigation for direct impacts to sensitive upland vegetation communities shall be implemented through on-site creation/enhancement of remaining sensitive upland vegetation communities and/or off-site acquisition, program funding, and/or mitigation bank credits. Mitigation acreages shall be implemented as shown in Table 10, Mitigation for Direct Impacts to Sensitive Vegetation Communities.

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Table MM-BIO-4. Mitigation for Direct Impacts to Sensitive Upland Vegetation Communities
Sensitive Vegetation Community
Direct
Impacts
(acres)
Mitigation
Ratio
Mitigation
(acres)
Coast Live Oak Woodland Alliance* 7.71 3:1 23.13
California Walnut Grove 0.01 3:1 0.03
Disturbed California Sagebrush
Scrub

0.91 1:1 0.91
Totals 8.63 — 23.33
* Excludes 1.78 acres of coast live oak woodland associated with jurisdictional waters Prior to the issuance of a grading permit or any earthwork on the Project site, a qualified biologist, subject to the City’s approval, shall prepare a Conceptual Restoration Plan (CRP) that sets forth the requirements for mitigating permanent and temporary impacts to sensitive upland vegetation communities (i.e., coast live oak woodland, California walnut grove woodland, and disturbed California sagebrush scrub) that is outside all jurisdictional water limits. Mitigation for sensitive vegetation communities associated with potential jurisdictional waters is identified in MM BIO-6. Areas of temporarily impacted sensitive vegetation communities on site shall be returned to similar conditions that existed prior to grading and/or ground-disturbing activities. Additional unimpacted areas in the Project site that support California annual non-native grassland may be enhanced to support existing sensitive native vegetation communities. The CRP shall include restoration of the following habitats:
▪ Upland Woodlands. Impacted areas of upland woodland (i.e., coast live oak woodland and California walnut grove woodland) shall be created/restored within and adjacent to the same on-site areas that the woodland currently existed prior to Project implementation, as well as other areas deemed to have appropriate soils and topography for successful establishment. Prior to vegetation removal activities, native acorns/nuts shall be collected. Understory areas shall be revegetated with a diversity of locally-collected seeds. Temporary irrigation shall be established and maintained, with irrigation suspensions in times of rainfall. Successful establishment of the woodland shall be determined only after removal of irrigation system and confirmed ability of the woodland to survive in the absence of irrigation. Mitigation for impacts to woodlands shall be implemented at a ratio of no less than 3:1 and shall be accomplished through a combination of on-site replacement and enhancement, onsite preservation, and off-site acquisition and/or mitigation bank credits. If feasible, woodlands would be created/restored at a minimum of 1:1 on-site, with the goal of increasing on-site restoration beyond 1:1.
▪ Sagebrush Scrub. Impacted areas of California sagebrush scrub shall be created within and adjacent to the same on-site areas that the scrub currently exist, as well as other areas deemed to have appropriate soils and topography for successful establishment.

Prior to grading activities, native and locally collected seeds shall be collected be planted onsite within the mitigation areas. Irrigation shall be provided, as necessary, to assure establishment of the scrub. Based upon the disturbed, low quality nature of Item #8. Page 542
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the existing California sagebrush scrub on site, mitigation of scrub shall be implemented at a ratio of no less than 1:1 and shall be accomplished through a combination of on-site replacement and enhancement, on-site preservation, and offsite acquisition and/or mitigation bank credits.

The CRP shall include a monitoring schedule, minimum performance standard of success, estimated costs, and identification of responsible entities. At a minimum, the CRP shall require a one-time restoration effort followed by monitoring and invasive weed removal for a minimum of five (5) years following ground-disturbing activities to compensate the direct temporary impacts. The monitoring program shall ensure successful establishment of the mitigation land, and if establishment is not realized within five years, restoration activities and monitoring may continue until minimum ratios as outlined above are established. The CRP shall be submitted to the City for review and shall revised to the satisfaction of the City..

MM-BIO-5 Indirect Impacts to Sensitive Vegetation Communities Flagging Limits. To prevent inadvertent disturbance to sensitive vegetation communities, including jurisdictional waters, outside the limits of work, the construction limits shall be clearly demarcated (e.g., installation of flagging or temporary high visibility construction fence) prior to ground disturbance activities. All construction activities including equipment staging and maintenance shall be conducted within the marked disturbance limits.

Monitoring. A qualified biologist, subject to the City’s approval, shall be present during initial ground-disturbing activities within the Project site to ensure that Project activities stay within the demarcated limits.

7.3 Impact BIO-3: Jurisdictional Wetlands and Waters
Significant direct and indirect impacts to jurisdictional waters can be mitigated to less than significant with implementation of the following measures:

MM-BIO-6 Mitigation for direct impacts to jurisdictional waters shall be implemented through on-site enhancement of remaining jurisdictional waters and/or off-site acquisition, program funding, and/or mitigation bank credits. Mitigation ratios for each type of jurisdictional waters is shown in Table 11, Mitigation for Direct Impacts to Potential Jurisdictional Waters.

Table MM-BIO-6. Mitigation for Direct Impacts to Potential Jurisdictional Waters
Jurisdictional Waters Type
Direct
Impacts
(acres)
Mitigation
Ratio
Mitigation
(acres)
USACE waters of the United States 0.38 1:1 0.38
RWQCB waters of the state 0.50 1:1 0.50
CDFW streambed and bank, with
coast live oak woodland

1.77 3:1 5.31
CDFW streambed and bank, with
non-riparian habitat*

0.28 1:1 0.28
* Parks and ornamental plantings, disturbed habitat, and developed-concrete channel Item #8. Page 543
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On-site Mitigation. Prior to the issuance of a grading permit or any earthwork on the Project site, the Project Applicant shall prepare a (Habitat Mitigation and Monitoring Plan) HMMP for on-site mitigation for temporary and permanent impacts to jurisdictional resources (including coast live oak woodlands associated with the drainages), which shall include habitat enhancement and creation activities. The HMMP shall at a minimum include a feasible implementation structure, salvage/seeding details, invasive species eradication methods, irrigation system and schedule, a monitoring schedule, performance standard of success, estimated costs, and identification of responsible entities. The HMMP shall include restoration of the following habitats associated with the potential CDFW jurisdictional limits:
• Riparian Coast Live Oak Woodland. Impacted areas of coast live oak woodland within the CDFW jurisdictional limits shall be created/restored within and adjacent to the same on-site areas that the woodland currently existed prior to Project implementation, as well as other areas deemed to have appropriate soils and topography for successful establishment. Prior to vegetation removal activities, native acorns/nuts shall be collected. Understory areas shall be revegetated with a diversity of locally collected seeds. Temporary irrigation shall be established and maintained, with irrigation suspensions in times of rainfall. Successful establishment of the woodland shall be determined only after removal of irrigation system and confirmed ability of the woodland to survive in the absence of irrigation. If feasible, woodlands would be created/restored at a minimum of 1:1 on-site, with the goal of increasing onsite restoration beyond 1:1.

At a minimum, the HMMP shall require a one-time restoration effort followed by monitoring and invasive weed removal for a minimum of five (5) years following ground-disturbing activities to compensate the direct temporary impacts. The monitoring program shall ensure successful establishment of the mitigation land, and if establishment is not realized within five years, restoration activities and monitoring may continue until minimum ratios as outlined above are established. On-site land shall be preserved in perpetuity through a deed restriction or conservation easement, and the HMMP shall identify an approach for funding assurance for the long-term management of the conserved land. The HMMP shall be submitted to CDFW, USACE, and RWQCB for review and comment, and revised to the satisfaction of the City and the three agencies for their approval.

Off-site Mitigation. If mitigation is implemented off-site, the Project Applicant shall work with the CDFW, USACE, and RWQCB to ensure the purchase of land acquisition, mitigation program funding, and/or mitigation bank credits are appropriate to offset permanent impacts.

Mitigation lands shall be comprised of similar or higher quality riparian woodland and preferably located in the vicinity of the site or watershed. Any off-site land acquisition shall be preserved in perpetuity through a deed restriction or conservation easement, and an HMMP shall be prepared that identifies an approach for funding assurance for the long-term management of the purchased land.

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7.4 Impact BIO-4: Habitat Linkages and Wildlife Corridors The Project site does not function as a wildlife corridor or habitat linkage and does not occur within any designated wildlife corridors of habitat linkages. Direct or indirect impacts to wildlife corridors and habitat connectivity are not anticipated; and would therefore, be less than significant.

7.5 Impact BIO-5: City of Glendora Protected Trees
Significant direct and indirect impacts to City protected trees can be mitigated to less than significant with implementation of the following measures:

MM-BIO-7 On-site Mitigation. Mitigation for City protected trees shall consider and overlap with any onsite compensation for special-status vegetation communities (MM-BIO-4 and MM-BIO-5) and jurisdictional waters (MM-BIO-6). Prior to the issuance of a grading permit or any earthwork on the Project site, a qualified arborist shall conduct a tree survey to confirm previous tree inventory data points and finalize the tree count for the purposes of replacement and shall prepare a protected Tree Planting And Maintenance Plan. The Plan shall be developed by a qualified arborist or landscape architect, subject to the City’s approval, and it shall identify tree planting locations, planting stock requirements, planting techniques, maintenance standards, tree protection standards, tree survival criteria, monitoring protocols, and reporting standards.

Minimum tree replacement to removal ratios shall be no less than the following for each trees diameter at breast height (dbh) in accordance with the City’s 2018 Urban Forestry Manual:

Native 8”-15” dbh 2:1 replacement
Native 16”-36” dbh 3:1 replacement
Native 37”-48” dbh 5:1 replacement
Native 49”-60” dbh 6:1 replacement
Native 61” dbh and up 7:1 replacement
Other 10”-15” dbh 1:1 replacement
Other 16”-36” dbh 1:1 replacement
Other 37”-48” dbh 2:1 replacement
Other 49”-60” dbh 3:1 replacement
Other 61” dbh and up 5:1 replacement
The plan shall be approved by the City prior to implementation.

Offsite Mitigation. For protected trees that are not replaced on-site, an in-lieu fee for future tree replacement shall be collected and deposited into a tree replacement fund. The in-lieu fee is based on the City’s cost to replant and set by City resolution.

MM-BIO-8 During Construction. Prior to issuance of the Project’s grading permit, the Applicant shall coordinate with LACFCD to assess the feasibility of oak tree preservation within the minimal grading/grooming areas and determine whether select trees could be preserved in place while maintaining the health and safety requirements of the LACFCD debris/flood control facility functions. Trees identified as being feasibly preserved and trees within approximately 15 feet of proposed construction activity shall be temporarily fenced with chain link or other material Item #8. Page 545
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satisfactory to City planning staff throughout grading and construction activities. The fencing shall be installed three feet outside of the dripline of each tree (or edge of canopy for cluster of trees), be four-foot-tall, and staked every six (6) feet. The fenced area shall be considered the tree protection zone (TPZ) unless proximate construction required temporary removal. An International Society of Arboriculture Certified arborist shall monitor any construction activity taking place within or near to the TPZ and shall submit a Construction Observation letter to the City for approval, prior to final inspection, summarizing the results of the monitoring activity and resulting health of trees designated for preservation on-site.

Post-Construction. For a period of no less than five (5) years from the date of final inspection, an International Society of Arboriculture Certified arborist shall submit to the City a monitoring report annually. The report shall show compliance with the tree protection conditions of approval and verification that all trees are in good health. Further, all trees that have been substantially root pruned (30% or more of their root zone) during construction within the TPZ shall be monitored by an International Society of Arboriculture Certified arborist for the first five years after construction completion. The arborist shall submit an annual report, photograph each tree and compare tree health and condition to the original, pre-construction baseline.

7.6 Level of Significance After Mitigation
Implementation of these mitigation measures will reduce potential impacts to biological resources to below a level of significance.

Two special-status reptiles (Southern California legless lizard and coastal whiptail) have occurred in the Study Area.

Construction activities associated with the proposed Project could cause direct mortality of these species. MM-BIO1 requires the development of a special-status wildlife relocation plan, pre-construction focused special-status wildlife surveys, and monitoring during initial ground-disturbing activities. Potential direct impacts to Southern California legless lizard and coastal whiptail would be less than significant with implementation of MM-BIO-1.

Construction activities associated with the proposed Project could result in a loss of suitable habitat or direct take of birds and are considered significant. MM-BIO-2 requires nesting bird surveys within 300 feet (500 feet for raptors) of the proposed impact areas and if active nests are found, the biologist shall establish buffers and/or implement monitoring to avoid impacting avian nesting success. Potential direct impacts to protected nesting birds would be less than significant with implementation of MM-BIO-2.

One special-status bat (hoary bat) has a moderate potential to occur in the Study Area. Construction activities associated with the proposed Project could cause direct mortality of these species. MM-BIO-3 requires seasonal avoidance, pre-construction roost survey, and roost monitoring. Potential direct impacts to hoary bat would be less than significant with implementation of MM-BIO-3.

Significant direct and indirect temporary and permanent impacts to sensitive vegetation communities (coast live oak woodland alliance, California walnut woodland, and disturbed California sagebrush scrub) would occur due to implementation of the Project. MM-BIO-4 requires that habitat compensation be completed by the purchase of credits from an agency-approved mitigation bank or purchase of in lieu credits from an in-lieu fee program and/or through the preparation and implementation of on-site habitat restoration plan. MM-BIO-5 avoids indirect impacts to sensitive vegetation communities by requiring the demarcation of the disturbance limits. Impacts to sensitive vegetation communities and jurisdictional waters would be less than significant with implementation of MM-BIO-4 and MM-BIO-5.

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Significant direct and indirect temporary and permanent impacts to potential jurisdictional waters would occur due to implementation of the Project. MM-BIO-6 requires that jurisdictional waters compensation be completed by the purchase of credits from an agency-approved mitigation bank or purchase of in lieu credits from an in-lieu fee program and/or through the preparation and implementation of on-site habitat restoration plan. MM-BIO-5 avoids indirect impacts to jurisdictional waters by requiring the demarcation of the disturbance limits. Impacts to jurisdictional waters would be less than significant with implementation of MM-BIO-5 and MM-BIO-6.

Direct impacts would occur, and indirect impacts may occur, to trees protected by the City. MM-BIO-7 requires the replacement of the removed trees per a City-defined ratio and the development of a planting and maintenance plan that will guide the maintenance and monitoring of the replacement trees. MM-BIO-8 requires fencing to shield protected trees located in close proximity to construction activities and requires monitoring of any construction activities taking place within or near to the TPZ. MM-BIO-8 also requires annual tree surveys and submission of an annual tree monitoring report for a period of no less than five years, with additional requirements for trees that have sustained substantial root zone pruning. Impacts to protected trees would be less than significant with implementation of MM-BIO-7 and MM-BIO-8.

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8375 53 MARCH 2022
8 References
American Ornithological Society. 2019. Check-List of North and Middle American Birds. Accessed February 2022. http://checklist.aou.org/.

USACE (U.S. Army Corps of Engineers). 1987. Corps of Engineers Wetlands Delineation Manual. Online ed.

Environmental Laboratory, Wetlands Research Program Technical Report Y-87-1. Vicksburg, Mississippi:

U.S. Army Engineer Waterways Experiment Station. January 1987. Accessed February 2022. http://www.fedcenter.gov/Bookmarks/index.cfm?id=6403&pge_id=1606.

USACE. 2008a. A Field Guide to the Identification of the Ordinary High Water Mark (OHWM) in the Arid West Region of the Western United States, A Delineation Manual. Cold Region Research and Environmental Laboratory, ERDC/CRREL TR-08-12. Hanover, New Hampshire: U.S. Army Engineer Research and Development Center. August 2008.

USACE. 2008b. Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Arid West Region (Version 2.0). Final Version. Environmental Laboratory, ERDC/EL TR-08-28. Vicksburg, Mississippi: U.S.

Army Engineer Research and Development Center. September 2008. Accessed February 2022. http://www.acoe.army.mil/Portals/2/docs/civilworks/regulatory/reg_supp/trel08-28.pdf.

USACE and EPA (U.S. Army Corps of Engineers and U.S. Environmental Protection Agency). 2008. “Clean Water Act Jurisdiction Following the U.S. Supreme Court’s Decision in Rapanos v. United States & Carabell v. United States.” December 2, 2008. Accessed February 2022. http://water.epa.gov/lawsregs/guidance/ wetlands/upload/2008_12_3_wetlands_CWA_Jurisdiction_Following_Rapanos120208.pdf.

Atwood, J.L., and D.R. Bontrager. 2001. California Gnatcatcher (Polioptila californica). In The Birds of North America No. 574, edited by A. Poole and F. Gill. Philadelphia, Pennsylvania: The Academy of Natural Sciences, and Washington, D.C.: American Ornithologists’ Union. Accessed February 2022. http://birds.audubon.org/species/calgna.

Atwood, J.L., S.H. Tsai, C.H. Reynolds, J.C. Luttrell, and M.R. Fugagli. 1998. Factors Affecting Estimates of California Gnatcatcher Territory Size. Western Birds 29:269–279.

Bennett, R.T. 2014. Tree Report for Glendora Heights (dated February 15, 2014).

Bennett, R.T. 2018. Tree Report for Glendora Heights (dated September 15, 2018).

Bennett, R.T. 2019. Tree Report for Glendora Heights (dated August 24, 2019).

CAL FIRE (California Department of Forestry and Fire Protection). 2014. Colby Fire Incident Information. Accessed February 2022. http://cdfdata.fire.ca.gov/incidents/incidents_details_info?incident_id=945.

Calflora. 2022. Information on California plants for education, research and conservation, with data contributed by public and private institutions and individuals, including the Consortium of California Herbaria [web application]. Berkeley, California: Calflora. Accessed February 2022. http://www.calflora.org/.

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GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 54 MARCH 2022
CDFW (California Department of Fish and Wildlife). 2018. California Natural Communities. January 2022.

Accessed February 2022. https://www.wildlife.ca.gov/Data/VegCAMP/Natural-Communities# sensitive%20natural%20communities.

CDFW. 2019a. RareFind 5, Version 5.2.14. Biogeographic Data Branch. Sacramento, California: California Natural Diversity Database. Accessed February 2022. https://map.dfg.ca.gov/rarefind/view/RareFind.aspx.

CDFW. 2019b. Natural Communities List Arranged Alphabetically by Life Form, dated November 8, 2019.

Accessed February 2022. https://nrm.dfg.ca.gov/FileHandler.ashx?DocumentID=153398&inline.

CDFW. 2019c. California Regional Conservation Plans [map]. April 2019. Accessed February 2022. https://www.wildlife.ca.gov/Conservation/Planning/NCCP.

California Department of Water Resources. 2016. Bulletin 118: California’s Groundwater. Accessed February 2022. https://water.ca.gov/Programs/Groundwater-Management/Bulletin-118.

Cal-IPC (California Invasive Plant Council). 2022. The Cal-IPC Inventory, online database. Accessed February 2022. https://www.cal-ipc.org/plants/inventory/.

Center for Biological Diversity and the Mountain Lion Foundation. 2019. A Petition to List the Southern California/Central Coast Evolutionarily Significant Unit (ESU) of Mountain Lions as Threatened under the California Endangered Species Act (CESA). Accessed January 2021. https://nrm.dfg.ca.gov/FileHandler. ashx?DocumentID=171208&inline.

CNPS (California Native Plant Society). 2022a. CNPS Rare Plant Rank. Accessed February 2022. https://www.cnps.org/rare-plants/cnps-rare-plant-ranks.

CNPS. 2022b. Inventory of Rare and Endangered Plants, online database. Accessed February 2022. http://www.rareplants.cnps.org/advanced.html.

City of Glendora. 2003. Tree Preservation Ordinance of 2003. City of Glendora Ordinance No. 1768: An Ordinance to Amend the Municipal Code to Create a New Tree Preservation Ordinance. Glendora Municipal Code, Title 16, Trees. January 14, 2003. Accessed February 2022. http://qcode.us/codes/glendora/.

City of Glendora. 2006a. Conservation Element. Glendora Community Plan 2025. http://www.ci.glendora.ca.us/ departments-services/planning/applications-documents/general-plan-specific-plans/glendora-general-plan.

City of Glendora. 2006b. Land Use Element. Glendora Community Plan 2025. https://www.cityofglendora.org/home/showpublisheddocument/7231/635193398301500000.

City of Glendora. 2018a. City of Glendora Community Services Department Urban Forestry Manual. Prepared by West Coast Arborists Inc. for the City of Glendora. Revised March 2018. Pp 55.

City of Glendora. 2018b. City of Glendora General Plan Land Use Map. Updated December 2018. https://www.cityofglendora.org/home/showpublisheddocument/25079/636887674982170000.

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County of Los Angeles. 2006. Final Program Environmental Impact Report: San Gabriel River Corridor Master Plan. SCH No. 2003041187. Prepared by MWH for the County of Los Angeles Department of Public Works. June 2006. http://ladpw.org/wmd/watershed/sg/mp/peir.cfm.

County of Los Angeles. 2014. Soil Types, GIS Data for LA County. Los Angeles County GIS Data Portal. Accessed February 2022. http://egis3.lacounty.gov/dataportal/2011/01/27/soil-types/.

EPA (U.S. Environmental Protection Agency). 2017. Watershed Assessment, Tracking and Environmental Results (WATERS). Accessed February 2022. https://www.epa.gov/waterdata/waters-watershed-assessmenttracking-environmental-results-system.

Faber-Langendoen, D., J. Nichols, L. Master, K. Snow, A. Tomaino, R. Bittman, G. Hammerson, B. Heidel, L.

Ramsay, A. Teucher, and B. Young. 2012. NatureServe Conservation Status Assessments: Methodology for Assigning Ranks. NatureServe, Arlington, VA.

Google. 2022. Google Earth desktop application. Accessed February 2022. https://www.google.com/earth/.

Holland, R.F. 1986. Preliminary Descriptions of the Terrestrial Natural Communities of California. NongameHeritage Program, California Department of Fish and Game. October 1986.

Jepson Flora Project. 2022. Jepson eFlora. Berkeley, California: University of California. Accessed February 2022. http://ucjeps.berkeley.edu/IJM.html.

LACDPW (Los Angeles County Department of Public Works). 2019. Precipitation. Accessed July 2019. http://ladpw.org/wrd/precip/.

Mock, P.J. 2004. California Gnatcatcher (Polioptila californica). In The Coastal Scrub and Chaparral Bird Conservation Plan: A Strategy for Protecting and Managing Coastal Scrub and Chaparral Habitats and Associated Birds in California. California Partners in Flight. http://www.prbo.org/calpif/htmldocs/ scrub.html.

Moyle, P.B. 2002. Inland Fishes of California. Revised and expanded. Berkeley, California: University of California Press, Berkeley and Los Angeles, 502 pp.

NETR (Nationwide Environmental Title Research). 2022. Historic Aerials. NETROnline. https://www.historicaerials.com/.

O’Leary, J.F. 1990a. Post-fire Diversity Patterns in Two Subassociations of California Coastal Sage Scrub. Journal of Vegetation Science1:173–180.

O’Leary, J.F. 1990b. California Coastal Sage Scrub: General Characteristics and Considerations for Biological Conservation. In Endangered Plant Communities of Southern California, edited by A. Schoenherr, 24–41.

Southern California Botanists, Special Publications No. 3.

Sawyer, J.O., T. Keeler-Wolf, and J.M. Evens. 2009. A Manual of California Vegetation. 2nd edition. Sacramento, California: California Native Plant Society.

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GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 56 MARCH 2022
Society for the Study of Amphibians and Reptiles. 2017. Checklist of the Standard English & Scientific Names of Amphibians & Reptiles. Accessed February 2022. https://ssarherps.org/publications/north-american-checklist/.

South Coast Wildlands. 2008. South Coast Missing Linkages: A Wildland Network for the South Coast Ecoregion.

Produced in cooperation with partners in the South Coast Missing Linkages Initiative. Accessed February 2022. http://www.scwildlands.org.

Spencer, W.D., P. Beier, K. Penrod, K. Winters, C. Paulman, H. Rustigian-Romsos, J. Strittholt, M. Parisi, and A.

Pettler. 2010. California Essential Habitat Connectivity Project: A Strategy for Conserving a Connected California. Prepared for California Department of Transportation, California Department of Fish and Game, and Federal Highways Administration. Accessed February 2022. http://nrm.dfg.ca.gov/FileHandler .ashx?DocumentID=18366.

USACE (U.S. Army Corps of Engineers). 2020. National Wetland Plant List, version 3.5. Accessed February 2022. http://wetland-plants.usace.army.mil/.

USDA NRCS (U.S. Department of Agriculture and Natural Resources Conservation Services). 2022a. Web Soil Survey [web application]. Accessed February 2022. http://websoilsurvey.nrcs.usda.gov/app/ HomePage.htm.

USDA NRCS. 2022b. PLANTS Database. Accessed February 2022. http://plants.usda.gov/java/.

USFWS. 1997. Coastal California Gnatcatcher (Polioptila californica californica) Presence/Absence Survey Guidelines. Carlsbad, California: USFWS. February 28, 1997.

USFWS. 2022a. Critical Habitat Mapper. Accessed February 2022. http://www.fws.gov/data.

USFWS. 2022b. Wetlands Mapper. Accessed February 2022. http://www.fws.gov/wetlands/Data/Mapper.html.

USGS (U.S. Geological Survey). 2018. 7.5-minute Glendora and Azusa quadrangle maps, Township 10 North, Range 6 West, and Section 4. Accessed February 2022. https://store.usgs.gov/map-locator.

USGS. 2022. National Hydrography Dataset: GIS Online viewer. Accessed February 2022. http://nhd.usgs.gov/.

Wilson, D.E., and D.M. Reeder, eds. 2005. Mammal Species of the World: A Taxonomic and Geographic Reference. 3rd ed. Online version. Baltimore, Maryland: Johns Hopkins University Press. Accessed February 2022. http://www.bucknell.edu/msw3/.

WRCC (Western Regional Climate Center). 2022. Azusa City Park Mean Annual Precipitation. Accessed February 2022. http://www.wrcc.dri.edu/cgi-bin/cliMAIN.pl?ca0410.

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SOURCE: USGS 7.5-Minute Quadrange, Azusa and Glendora CA Township 01N, Range 10W, Section 24
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FIGURE 2
Tentative Tract Map No. 72413
Grand Estates Project
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60 MARCH 2022

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SOURCE: County of Los Angeles 2018; USGS NHD 2018; USFWS NWI 2018; Bing Maps 2018 Date: 12/19/2019 - Last saved by: cstarbird - Path: Z:\Projects\j837501\MAPDOC\DOCUMENT\BTR\Fig_Hydro_Setting.mxd 0 150 300
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FIGURE 
Hydrogeologic Setting
Grand Estates Project
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SOURCE: Bing Maps 2018
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Project BoundaryACOE/RWQCB Jurisdictional FeatureCDFW Jurisdictional Feature Vegetation Communities and Land Covers
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Grand Estates Project
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FIGURE 7
Impacts to Biological Resources
Grand Estates Project
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Appendix A
Representative Site Photographs
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APPENDIX A. REPRESENTATIVE SITE PHOTOS

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 A-1
FEBRUARY 2022
Photo 1. Coast live oak woodland in Drainage A. Photo 2. California walnut grove in the foreground and coast live oak woodland in the background
within Drainage B.

Photo 3. Disturbed California sagebrush scrub
adjacent to the concrete Drainage E.

Photo 4. Non-native grassland in the open space
portion of the Study Area with Drainage A and
coast live oak woodland in the middle.

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APPENDIX A. REPRESENTATIVE SITE PHOTOS

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 A-2
FEBRUARY 2022
Photo 5. Non-native grassland in the area proposed
for residential lots, with coast live oak woodland in
the background.

Photo 6. Ornamental land cover adjacent to the
concrete Drainage E.

Photo 7. Coast live oak woodland on the ridge
between Drainage A and Drainage D.

Photo 8. The weir at the southern end of Drainage
A.

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APPENDIX A. REPRESENTATIVE SITE PHOTOS

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 A-3
FEBRUARY 2022
Photo 9. The weir at the southern end of Drainage
D.

Photo 10. The weir at the southern end of the
earthen bottom portion of Drainage E.

Photo 11. Ornamental landscaping with a nonnative grass understory in the southern end of the Study Area.

Photo 12. Non-native grassland in the central
portion of the area proposed for residential lots.

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APPENDIX A. REPRESENTATIVE SITE PHOTOS

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 A-4
FEBRUARY 2022

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Appendix B
Plant Species Compendium
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APPENDIX B. PLANT COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 1
FEBRUARY 2022
* signifies introduced (non-native) species

VASCULAR SPECIES
DICOTS
ADOXACEAE—MUSKROOT FAMILY
Sambucus nigra ssp. caerulea—blue elderberry
AMARANTHACEAE—AMARANTH FAMILY
Amaranthus blitoides—mat amaranth
Amaranthus californicus—California amaranth
ANACARDIACEAE—SUMAC OR CASHEW FAMILY
* Schinus molle—Peruvian peppertree
Malosma laurina—laurel sumac
Rhus ovata—sugar sumac
Toxicodendron diversilobum—Pacific poison oak
APOCYNACEAE—DOGBANE FAMILY
* Nerium oleander—oleander
* Vinca major—bigleaf periwinkle
Funastrum cynanchoides var. hartwegii—Hartweg’s twinevine ARALIACEAE—GINSENG FAMILY
* Hedera helix—English ivy
ASTERACEAE—SUNFLOWER FAMILY
Ambrosia acanthicarpa—flatspine bur ragweed
Ambrosia confertiflora—weakleaf bur ragweed
Artemisia californica—coastal sagebrush
Artemisia douglasiana—Douglas’ sagewort
Artemisia dracunculus—wild tarragon
Baccharis salicifolia—mule-fat
Brickellia californica—California brickellbush
* Carduus pycnocephalus ssp. pycnocephalus—Italian plumeless thistle * Centaurea melitensis—Maltese star-thistle
Chaenactis glabriuscula—yellow pincushion
* Cirsium vulgare—bull thistle
Encelia farinosa—brittlebush
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APPENDIX B. PLANT COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 2
FEBRUARY 2022
Erigeron canadensis—Canadian horseweed
Eriophyllum confertiflorum—golden-yarrow
Helianthus annuus—common sunflower
* Helminthotheca echioides—bristly oxtongue
Heterotheca grandiflora—telegraphweed
* Lactuca serriola—prickly lettuce
* Logfia gallica—narrowleaf cottonrose
Lepidospartum squamatum—scale broom
Malacothrix saxatilis—cliff desertdandelion
Pseudognaphalium biolettii—two-color rabbit-tobacco
Pseudognaphalium californicum—ladies’ tobacco
* Silybum marianum—blessed milkthistle
* Sonchus asper—spiny sowthistle
* Sonchus oleraceus—common sowthistle
* Taraxacum officinale—common dandelion
BORAGINACEAE—BORAGE FAMILY
Phacelia cicutaria—caterpillar phacelia
Phacelia distans—distant phacelia
Phacelia minor—wild Canterbury bells
Pholistoma auritum—blue fiestaflower
BRASSICACEAE—MUSTARD FAMILY
* Brassica nigra—black mustard
* Brassica rapa—field mustard
* Hirschfeldia incana—shortpod mustard
* Sisymbrium irio—London rocket
* Sisymbrium officinale—hedgemustard
CACTACEAE—CACTUS FAMILY
* Opuntia ficus-indica—Barbary fig
Opuntia littoralis—coastal prickly pear
CARYOPHYLLACEAE—PINK FAMILY
* Cerastium glomeratum—sticky chickweed
* Stellaria media—common chickweed
CHENOPODIACEAE—GOOSEFOOT FAMILY
* Chenopodium berlandieri—pitseed goosefoot
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APPENDIX B. PLANT COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 3
FEBRUARY 2022
Chenopodium californicum—California goosefoot
* Chenopodium murale—nettleleaf goosefoot
* Salsola tragus—prickly Russian thistle
CONVOLVULACEAE—MORNING-GLORY FAMILY
Calystegia macrostegia—island false bindweed
* Convolvulus arvensis—field bindweed
Cuscuta californica—chaparral dodder
CUCURBITACEAE—GOURD FAMILY
Marah macrocarpa—Cucamonga manroot
EUPHORBIACEAE—SPURGE FAMILY
Croton setiger—dove weed
Euphorbia melanadenia—red-gland spurge
* Euphorbia prostrata—prostrate sandmat
* Euphorbia peplus—petty spurge
* Ricinus communis—castorbean
FABACEAE—LEGUME FAMILY
Acmispon glaber var. glaber—common deerweed
Acmispon wrangelianus—Chilean bird’s-foot trefoil
Lathyrus vestitus var. alefeldii—Alefeld’s pea
Lupinus hirsutissimus—stinging annual lupine
Lupinus longifolius—longleaf bush lupine
Lupinus succulentus—hollowleaf annual lupine
* Medicago polymorpha—burclover
* Melilotus albus—yellow sweetclover
* Melilotus indicus—annual yellow sweetclover
* Vicia villosa—winter vetch
FAGACEAE—OAK FAMILY
Quercus agrifolia—California live oak
GERANIACEAE—GERANIUM FAMILY
* Erodium cicutarium—redstem stork’s bill
JUGLANDACEAE—WALNUT FAMILY
Juglans californica—Southern California black walnut
Item #8. Page 576
Meeting Date: 1/24/2023 / Packet Page #: 641
APPENDIX B. PLANT COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 4
FEBRUARY 2022
LAMIACEAE—MINT FAMILY
* Marrubium vulgare—horehound
Salvia apiana—white sage
LOASACEAE—LOASA FAMILY
Mentzelia micrantha—San Luis blazingstar
MALVACEAE—MALLOW FAMILY
* Malva parviflora—cheeseweed mallow
MORACEAE—MULBERRY FAMILY
* Ficus carica—edible fig
MYRSINACEAE—MYRSINE FAMILY
* Anagallis arvensis—scarlet pimpernel
MYRTACEAE—MYRTLE FAMILY
* Eucalyptus camaldulensis—river redgum
* Eucalyptus citriodora—lemonscented gum
* Eucalyptus sideroxylon—red ironbark
NYCTAGINACEAE—FOUR O’CLOCK FAMILY
* Bougainvillea spectabilis—great bougainvillea
Mirabilis laevis var. crassifolia—California four o’clock OLEACEAE—OLIVE FAMILY
* Olea europaea—olive
OXALIDACEAE—OXALIS FAMILY
* Oxalis pes-caprae—Bermuda buttercup
PHRYMACEAE—LOPSEED FAMILY
Diplacus aurantiacus—orange bush monkeyflower
PHYTOLACCACEAE—POKEWEED FAMILY
* Phytolacca americana—American pokeweed
PLATANACEAE—PLANE TREE, SYCAMORE FAMILY
Platanus racemosa—California sycamore
Item #8. Page 577
Meeting Date: 1/24/2023 / Packet Page #: 642
APPENDIX B. PLANT COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 5
FEBRUARY 2022
POLYGONACEAE—BUCKWHEAT FAMILY
Eriogonum fasciculatum—Eastern Mojave buckwheat
PROTEACEAE—PROTEA FAMILY
* Grevillea robusta—silkoak
RHAMNACEAE—BUCKTHORN FAMILY
Frangula californica — California coffee berry
ROSACEAE—ROSE FAMILY
Heteromeles arbutifolia—toyon
Prunus ilicifolia ssp. ilicifolia—hollyleaf cherry
Rubus ursinus—California blackberry
RUBIACEAE—MADDER FAMILY
Galium angustifolium—narrowleaf bedstraw
Galium aparine—stickywilly
Galium porrigens—graceful bedstraw
SAPINDACEAE—SOAPBERRY FAMILY
Cupaniopsis anacardioides—carrotwood
SIMAROUBACEAE—QUASSIA OR SIMAROUBA FAMILY
* Ailanthus altissima—tree of heaven
SOLANACEAE—NIGHTSHADE FAMILY
Datura wrightii—sacred thorn-apple
* Nicotiana glauca—tree tobacco
Solanum douglasii—greenspot nightshade
Solanum parishii—Parish's nightshade
TROPAEOLACEAE—NASTURTIUM FAMILY
* Tropaeolum majus—nasturtium
URTICACEAE—NETTLE FAMILY
* Urtica urens—dwarf nettle
ZYGOPHYLLACEAE—CALTROP FAMILY
* Tribulus terrestris—puncturevine

Item #8. Page 578
Meeting Date: 1/24/2023 / Packet Page #: 643
APPENDIX B. PLANT COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 6
FEBRUARY 2022

FERNS AND FERN ALLIES
DRYOPTERIDACEAE—WOOD FERN FAMILY
Dryopteris arguta—coastal woodfern

GYMNOSPERMS AND GNETOPHYTES
PINACEAE—PINE FAMILY
* Pinus pinea—Italian stone pine
Pinus ponderosa—ponderosa pine

MONOCOTS
AGAVACEAE—AGAVE FAMILY
* Agave americana—American century plant
Hesperoyucca whipplei—chaparral yucca
ARECACEAE—PALM FAMILY
* Phoenix canariensis—Canary Island date palm
* Washingtonia robusta—Washington fan palm
POACEAE—GRASS FAMILY
* Arundo donax—giant reed
* Avena barbata—slender oat
* Avena fatua—wild oat
* Bromus diandrus—ripgut brome
* Bromus hordeaceus—soft brome
* Bromus madritensis—compact brome
* Cynodon dactylon—Bermudagrass
* Digitaria sanguinalis—hairy crabgrass
Elymus condensatus—giant wildrye
Elymus glaucus—blue wildrye
* Hordeum murinum—mouse barley
* Lamarckia aurea—goldentop grass
Melica imperfecta—smallflower melicgrass
* Pennisetum setaceum—crimson fountaingrass
* Stipa miliacea—no common name
Item #8. Page 579
Meeting Date: 1/24/2023 / Packet Page #: 644
Appendix C
Wildlife Species Compendium
Item #8. Page 580
Meeting Date: 1/24/2023 / Packet Page #: 645
Item #8. Page 581
Meeting Date: 1/24/2023 / Packet Page #: 646
APPENDIX C. WILDLIFE COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 C-1
FEBRUARY 2022
* signifies introduced (non-native) species

REPTILE

LIZARDS
PHRYNOSOMATIDAE—IGUANID LIZARDS
Sceloporus occidentalis longipes—western fence lizard
SNAKES
COLUBRIDAE—COLUBRID SNAKES
Coluber lateralis lateralis—striped racer
BIRD

BLACKBIRDS, ORIOLES, AND ALLIES
ICTERIDAE—BLACKBIRDS
Icterus cucullatus—hooded oriole

BUSHTITS
AEGITHALIDAE—LONG-TAILED TITS AND BUSHTITS
Psaltriparus minimus—bushtit

CARDINALS, GROSBEAKS, AND ALLIES
CARDINALIDAE—CARDINALS AND ALLIES
Pheucticus melanocephalus—black-headed grosbeak
Piranga ludoviciana—western tanager

FINCHES
FRINGILLIDAE—FRINGILLINE AND CARDUELINE FINCHES AND ALLIES Carpodacus mexicanus—house finch
Spinus psaltria—lesser goldfinch

FLYCATCHERS
TYRANNIDAE—TYRANT FLYCATCHERS
Contopus sordidulus—western wood-pewee
Item #8. Page 582
Meeting Date: 1/24/2023 / Packet Page #: 647
APPENDIX C. WILDLIFE COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 C-2
FEBRUARY 2022
Empidonax difficilis—Pacific-slope flycatcher
Myiarchus cinerascens—ash-throated flycatcher
Tyrannus verticalis—western kingbird
Tyrannus vociferans—Cassin’s kingbird
HAWKS
ACCIPITRIDAE—HAWKS, KITES, EAGLES, AND ALLIES
Accipiter cooperii—Cooper’s hawk
Buteo jamaicensis—red-tailed hawk
Buteo lineatus—red-shouldered hawk

HUMMINGBIRDS
TROCHILIDAE—HUMMINGBIRDS
Calypte anna—Anna’s hummingbird
Calypte costae—Costa’s hummingbird
Selasphorus sasin—Allen’s hummingbird

JAYS, MAGPIES AND CROWS
CORVIDAE—CROWS AND JAYS
Aphelocoma californica—California scrub-jay
Corvus brachyrhynchos—American crow
Corvus corax—common raven

KINGLETS
REGULIDAE—KINGLETS
Regulus calendula—ruby-crowned kinglet

MOCKINGBIRDS AND THRASHERS
MIMIDAE—MOCKINGBIRDS AND THRASHERS
Mimus polyglottos—northern mockingbird

NEW WORLD VULTURES
CATHARTIDAE—CARDINALS AND ALLIES
Cathartes aura—turkey vulture
Item #8. Page 583
Meeting Date: 1/24/2023 / Packet Page #: 648
APPENDIX C. WILDLIFE COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 C-3
FEBRUARY 2022

OLD WORLD WARBLERS AND GNATCATCHERS
SYLVIIDAE—SYLVIID WARBLERS
Polioptila caerulea—blue-gray gnatcatcher

PIGEONS AND DOVES
COLUMBIDAE—PIGEONS AND DOVES
Patagioenas fasciata—band-tailed pigeon
Zenaida macroura—mourning dove

SILKY FLYCATCHERS
PTILOGONATIDAE—SILKY-FLYCATCHERS
Phainopepla nitens—phainopepla

STARLINGS AND ALLIES
STURNIDAE—STARLINGS
* Sturnus vulgaris—European starling
SWIFTS
APODIDAE—SWIFTS
Aeronautes saxatalis—white-throated swift

TITMICE
PARIDAE—CHICKADEES AND TITMICE
Baeolophus inornatus—oak titmouse

WOOD WARBLERS AND ALLIES
PARULIDAE—WOOD-WARBLERS
Oreothlypis ruficapilla—Nashville warbler
Oreothlypis celata—orange-crowned warbler
Cardellina pusilla—Wilson’s warbler
Setophaga coronata—yellow-rumped warbler
Setophaga petechia—yellow warbler

Item #8. Page 584
Meeting Date: 1/24/2023 / Packet Page #: 649
APPENDIX C. WILDLIFE COMPENDIUM

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 C-4
FEBRUARY 2022

WOODPECKERS
PICIDAE—WOODPECKERS AND ALLIES
Melanerpes formicivorus—acorn woodpecker
Picoides nuttallii—Nuttall’s woodpecker
WRENS
TROGLODYTIDAE—WRENS
Thryomanes bewickii—Bewick’s wren
Troglodytes aedon—house wren

WRENTITS
TIMALIIDAE—BABBLERS
Chamaea fasciata—wrentit

NEW WORLD SPARROWS
PASSERELLIDAE—NEW WORLD SPARROWS
Melospiza melodia—song sparrow
Melozone crissalis—California towhee
Pipilo maculatus—spotted towhee
MAMMAL
CANIDS
CANIDAE—WOLVES AND FOXES
Canis latrans—Coyote

SQUIRRELS
SCIURIDAE—SQUIRRELS
Sciurus griseus—Western gray squirrel
Spermophilus (Otospermophilus) beecheyi—California ground squirrel

UNGULATES
CERVIDAE—DEERS
Odocoileus hemionus—Mule deer
Item #8. Page 585
Meeting Date: 1/24/2023 / Packet Page #: 650
Appendix D
Assessment of Special-Status Plant Species Potentially
Occurring in the Study Area
Item #8. Page 586
Meeting Date: 1/24/2023 / Packet Page #: 651
Item #8. Page 587
Meeting Date: 1/24/2023 / Packet Page #: 652
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-1
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Arctostaphylos
glandulosa ssp.
gabrielensis
San Gabriel
manzanita
None/None/1B.2 Chaparral (rocky)/perennial evergreen
shrub/Mar/1950–4920
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Astragalus
brauntonii
Braunton's
milk-vetch
FE/None/1B.1 Chaparral, Coastal scrub, Valley and
foothill grassland; recent burns or
disturbed areas, usually sandstone
with carbonate layers/perennial
herb/Jan–Aug/10–2100
Low potential to occur. Marginal
habitat (coastal scrub) is present,
but the species distribution is very
limited in the San Gabriel
Mountains (Monrovia Canyon). The
species was not observed during
the focused special-status plant
species surveys in the Study Area.

Astragalus
lentiginosus var.
antonius
San Antonio
milk-vetch
None/None/1B.3 Lower montane coniferous forest,
Upper montane coniferous
forest/perennial herb/Apr–July/4920–
8530
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Astragalus
leucolobus
Big Bear
Valley
woollypod
None/None/1B.2 Lower montane coniferous forest,
Pebble (Pavement) plain, Pinyon and
juniper woodland, Upper montane
coniferous forest; rocky/perennial
herb/May–July/3605–9465
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Berberis nevinii Nevin's
barberry
FE/SE/1B.1 Chaparral, Cismontane woodland,
Coastal scrub, Riparian scrub; sandy or
gravelly/perennial evergreen
shrub/(Feb)Mar–June/225–2705
Low potential to occur. Suitable
associated habitat present and
recent local records occur, but the
conspicuous shrub was not
observed during the focused
special-status plant species survey
in the Study Area.

Botrychium
crenulatum
scalloped
moonwort
None/None/2B.2 Bogs and fens, Lower montane
coniferous forest, Meadows and seeps,
Marshes and swamps (freshwater),
Upper montane coniferous
forest/perennial rhizomatous
herb/June–Sep/4160–10760
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Item #8. Page 588
Meeting Date: 1/24/2023 / Packet Page #: 653
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-2
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Brodiaea filifolia thread-leaved
brodiaea
FT/SE/1B.1 Chaparral (openings), Cismontane
woodland, Coastal scrub, Playas, Valley
and foothill grassland, Vernal pools;
often clay/perennial bulbiferous
herb/Mar–June/80–3675
Not expected to occur. Associated
habitat (coastal scrub) is present
and recent local records occur, but
this species is usually found in
herbaceous plant communities
such as valley needlegrass
grassland, valley sacaton grassland,
nonnative grassland, alkali playa,
southern interior basalt vernal
pools, San Diego mesa hardpan
vernal pools, and San Diego mesa
claypan vernal pools in association
with coastal sage scrub in some
locations. These herbaceous
communities occur in open areas
on clay soils, soil with clay
subsurface, or clay lenses within
loamy, silty loam, loamy sand, silty
deposits with cobbles or alkaline
soils (USFWS 2009). These
conditions do not occur in the Study
Area.

Calochortus
clavatus var.
gracilis
slender
mariposa lily
None/None/1B.2 Chaparral, Coastal scrub, Valley and
foothill grassland/perennial
bulbiferous herb/Mar–
June(Nov)/1045–3280
Low potential to occur. Suitable
associated habitat is present, but
the species was not observed
during the focused special-status
plant species surveys in the Study
Area.

Calochortus
palmeri var.
palmeri
Palmer's
mariposa lily
None/None/1B.2 Chaparral, Lower montane coniferous
forest, Meadows and seeps;
mesic/perennial bulbiferous
herb/Apr–July/2325–7840
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Item #8. Page 589
Meeting Date: 1/24/2023 / Packet Page #: 654
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-3
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Calochortus
striatus
alkali
mariposa lily
None/None/1B.2 Chaparral, Chenopod scrub, Mojavean
desert scrub, Meadows and seeps;
alkaline, mesic/perennial bulbiferous
herb/Apr–June/225–5235
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
range of the species (western
Mojave Desert).

Calochortus weedii
var. intermedius
intermediate
mariposa lily
None/None/1B.2 Chaparral, Coastal scrub, Valley and
foothill grassland; rocky,
calcareous/perennial bulbiferous
herb/May–July/340–2805
Low potential to occur. Marginal
habitat (coastal scrub) is present,
but the species has a single record
from the San Gabriel Mountains.

Records for the species are
primarily associated with the
Puente Hills, the Santa Ana
Mountains, and the Perris Basin.

The species was not observed
during the focused special-status
plant species surveys in the Study
Area.

Calystegia felix lucky morninggloryNone/None/1B.1 Meadows and seeps (sometimes alkaline), Riparian scrub (alluvial);
historically associated with wetland
and marshy places, but possibly in
drier situations as well; possibly silty
loam and alkaline/annual rhizomatous
herb/Mar–Sep/95–705
Not expected to occur. Only one
record within the last 100 years in
Los Angeles County, with the
remaining recent occurrences from
Chino in San Bernardino County.

Carex occidentalis western sedge None/None/2B.3 Lower montane coniferous forest, Meadows and seeps/perennial
rhizomatous herb/June–Aug/5395–
10285
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Castilleja gleasoni Mt. Gleason
paintbrush
None/SR/1B.2 Chaparral, Lower montane coniferous
forest, Pinyon and juniper woodland;
granitic/perennial herb
(hemiparasitic)/May–
June(Sep)/2180–7120
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Item #8. Page 590
Meeting Date: 1/24/2023 / Packet Page #: 655
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-4
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Centromadia parryi
ssp. australis
southern
tarplant
None/None/1B.1 Marshes and swamps (margins), Valley
and foothill grassland (vernally mesic),
Vernal pools/annual herb/May–
Nov/0–1575
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Centromadia
pungens ssp. laevis
smooth
tarplant
None/None/1B.1 Chenopod scrub, Meadows and seeps,
Playas, Riparian woodland, Valley and
foothill grassland; alkaline/annual
herb/Apr–Sep/0–2100
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Chorizanthe parryi
var. parryi
Parry's
spineflower
None/None/1B.1 Chaparral, Cismontane woodland,
Coastal scrub, Valley and foothill
grassland; sandy or rocky,
openings/annual herb/Apr–
June/900–4005
Low potential to occur. Marginally
suitable habitat (coastal scrub) is
present, but the species was not
observed during the focused
special-status plant species surveys
in the Study Area.

Cladium
californicum
California
sawgrass
None/None/2B.2 Meadows and seeps, Marshes and
swamps Alkaline or
Freshwater/perennial rhizomatous
herb/June–Sep/195–5250
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Claytonia peirsonii
ssp. peirsonii
Peirson’s
spring beauty
None/None/1B.2 Subalpine coniferous forest, upper
montane coniferous forest; granitic,
metamorphic, scree, talus/perennial
herb/(Mar) May–June/4,950–9,005
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Dodecahema
leptoceras
slenderhorned
spineflower
FE/SE/1B.1 Chaparral, Cismontane woodland,
Coastal scrub (alluvial fan);
sandy/annual herb/Apr–June/655–
2495
Low potential to occur. Suitable
associated habitat (coastal scrub) is
present but the species is typically
associated with large floodplain
habitats categorized as alluvial
scrub (CDFW 2014).

Drymocallis
cuneifolia var.
ewanii
Ewan's
woodbeauty
None/None/1B.3 Lower montane coniferous forest (near
seeps and springs), Meadows and
seeps/perennial herb/June–
July/6230–7875
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Item #8. Page 591
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APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-5
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Dudleya cymosa
ssp. crebrifolia
San Gabriel
River dudleya
None/None/1B.2 Chaparral (granitic)/perennial
herb/Apr–July/900–1500
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Dudleya densiflora San Gabriel
Mountains
dudleya
None/None/1B.1 Chaparral, Cismontane woodland,
Coastal scrub, Lower montane
coniferous forest, Riparian woodland;
granitic, cliffs and canyon
walls/perennial herb/Mar–June/800–
2000
Not expected to occur. Suitable
associated habitat (granitic, cliffs
and canyon walls) is not present in
the Study Area.

Dudleya multicaulis manystemmed
dudleya
None/None/1B.2 Chaparral, Coastal scrub, Valley and
foothill grassland; often clay/perennial
herb/Apr–July/45–2590
Not expected to occur. Suitable
associated habitat (clay soils) is not
present in the Study Area.

Eriogonum
kennedyi var.
alpigenum
southern
alpine
buckwheat
None/None/1B.3 Alpine boulder and rock field,
Subalpine coniferous forest; granitic,
gravelly/perennial herb/July–
Sep/8530–11485
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Eriogonum
microthecum var.
johnstonii
Johnston's
buckwheat
None/None/1B.3 Subalpine coniferous forest, Upper
montane coniferous forest;
rocky/perennial deciduous
shrub/July–Sep/6000–9600
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Fimbristylis
thermalis
hot springs
fimbristylis
None/None/2B.2 Meadows and seeps (alkaline, near
hot springs)/perennial rhizomatous
herb/July–Sep/360–4395
Not expected to occur. Suitable
associated habitat (alkaline, near
hot springs) is not present.

Galium grande San Gabriel
bedstraw
None/None/1B.2 Broadleafed upland forest, Chaparral,
Cismontane woodland, Lower montane
coniferous forest/perennial deciduous
shrub/Jan–July/1390–4920
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Horkelia cuneata
var. puberula
mesa horkelia None/None/1B.1 Chaparral (maritime), Cismontane woodland, Coastal scrub; sandy or
gravelly/perennial herb/Feb–
July(Sep)/225–2655
Low potential to occur. Suitable
associated habitat (coastal scrub) is
present, but the species was not
observed during the focused
special-status plant species surveys
in the Study Area.

Item #8. Page 592
Meeting Date: 1/24/2023 / Packet Page #: 657
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-6
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Imperata brevifolia California
satintail
None/None/2B.1 Chaparral, Coastal scrub, Mojavean
desert scrub, Meadows and seeps
(often alkali), Riparian scrub;
mesic/perennial rhizomatous
herb/Sep–May/0–3985
Low potential to occur Suitable
associated habitat present and
recent local records occur, but the
conspicuous shrub was not
observed during the focused
special-status plant species survey
in the Study Area.

Juncus nodosus knotted rush None/None/2B.3 Meadows and seeps (mesic), Marshes and swamps (lake margins)/perennial
rhizomatous herb/July–Sep/95–6495
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Lewisia brachycalyx short-sepaled
lewisia
None/None/2B.2 Lower montane coniferous forest,
Meadows and seeps; mesic/perennial
herb/(Feb)Apr–June(July)/4490–7545
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Lilium parryi lemon lily None/None/1B.2 Lower montane coniferous forest, Meadows and seeps, Riparian forest,
Upper montane coniferous forest;
mesic/perennial bulbiferous
herb/July–Aug/4000–9005
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Linanthus
concinnus
San Gabriel
linanthus
None/None/1B.2 Chaparral, Lower montane coniferous
forest, Upper montane coniferous
forest; rocky, openings/annual
herb/Apr–July/4985–9185
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Lupinus peirsonii Peirson's
lupine
None/None/1B.3 Joshua tree woodland, Lower montane
coniferous forest, Pinyon and juniper
woodland, Upper montane coniferous
forest; gravelly or rocky/perennial
herb/Apr–June/3280–8200
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Monardella
macrantha ssp.
hallii
Hall's
monardella
None/None/1B.3 Broadleafed upland forest, Chaparral,
Cismontane woodland, Lower montane
coniferous forest, Valley and foothill
grassland/perennial rhizomatous
herb/June–Oct/2395–7200
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Item #8. Page 593
Meeting Date: 1/24/2023 / Packet Page #: 658
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-7
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Muhlenbergia utilis aparejo grass None/None/2B.2 Meadows and seeps, marshes and swamps, chaparral, coastal scrub,
cismontane woodland; sometimes
alkaline, sometimes
serpentinite/perennial rhizomatous
herb/Mar–Oct/82–7,625
Not expected to occur. The one
record of the species from the
region is from 1916, believed
extirpated, and is an outlier of the
other records in California (Coastal
Range and Death Valley region).

Navarretia
prostrata
prostrate
vernal pool
navarretia
None/None/1B.1 Coastal scrub, Meadows and seeps,
Valley and foothill grassland (alkaline),
Vernal pools; Mesic/annual herb/Apr–
July/5–3970
Not expected to occur. The species
is almost exclusively associated
with vernal pools in southern
California, which are not found
onsite.

Nemacladus
secundiflorus var.
robbinsii
Robbins'
nemacladus
None/None/1B.2 Chaparral, Valley and foothill
grassland; openings/annual herb/Apr–
June/1145–5575
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Opuntia basilaris
var. brachyclada
short-joint
beavertail
None/None/1B.2 Chaparral, Joshua tree woodland,
Mojavean desert scrub, Pinyon and
juniper woodland/perennial stem
succulent/Apr–June(Aug)/1390–5905
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
range of the species (northern
slopes of the San Gabriel and San
Bernardino mountains.

Oreonana vestita woolly
mountainparsley
None/None/1B.3 Lower montane coniferous forest,
Subalpine coniferous forest, Upper
montane coniferous forest; gravel or
talus/perennial herb/Mar–Sep/5295–
11485
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Orobanche valida
ssp. valida
Rock Creek
broomrape
None/None/1B.2 Chaparral, Pinyon and juniper
woodland; granitic/perennial herb
(parasitic)/May–Sep/4100–6560
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Oxytropis oreophila
var. oreophila
rock-loving
oxytrope
None/None/2B.3 Alpine boulder and rock field,
Subalpine coniferous forest; gravelly or
rocky/perennial herb/June–
Sep/11,150–12,465
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Item #8. Page 594
Meeting Date: 1/24/2023 / Packet Page #: 659
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-8
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Parnassia cirrata
var. cirrata
San
Bernardino
grass-ofParnassus
None/None/1B.3 Lower montane coniferous forest,
Meadows and seeps, Upper montane
coniferous forest; mesic, streamsides,
sometimes calcareous/perennial
herb/Aug–Sep/4,100–8,005
Not expected to occur. Suitable
associated habitat is not present,
and the Study Area is outside the
elevation range of the species.

Phacelia stellaris Brand's star
phacelia
None/None/1B.1 Coastal dunes, Coastal scrub/annual
herb/Mar–June/0–1310
Not expected to occur. Marginally
suitable associated habitat (coastal
scrub) is present, but the species is
only known has no records less
than 75 years old in Los Angeles
County.

Pseudognaphalium
leucocephalum
white rabbittobacco
None/None/2B.2 Chaparral, Cismontane woodland,
Coastal scrub, Riparian woodland;
sandy, gravelly/perennial
herb/(July)Aug–Nov(Dec)/0–6890
Low potential to occur. Suitable
habitat (coastal scrub and riparian
woodland) is present, but the
species has only one record within
the last 75 year within the San
Gabriel River. The species was not
observed during the focused
special-status plant species surveys
in the Study Area.

Senecio aphanactis chaparral
ragwort
None/None/2B.2 Chaparral, Cismontane woodland,
Coastal scrub; sometimes
alkaline/annual herb/Jan–
Apr(May)/45–2625
Low potential to occur. Suitable
habitat (coastal scrub and streams)
is present, but the species was not
observed during the focused
special-status plant species surveys
in the Study Area.

Sidalcea
neomexicana
salt spring
checkerbloom
None/None/2B.2 Chaparral, Coastal scrub, Lower
montane coniferous forest, Mojavean
desert scrub, Playas; alkaline,
mesic/perennial herb/Mar–June/45–
5020
Not expected to occur. Suitable soil
conditions are not present in the
Study Area.

Item #8. Page 595
Meeting Date: 1/24/2023 / Packet Page #: 660
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-9
FEBRUARY 2022
Scientific Name
Common
Name
Status1
(Federal/State/CRPR)
Primary Habitat Associations/
Life Form/ Blooming Period/
Elevation Range (feet) Potential to Occur
Symphyotrichum
defoliatum
San
Bernardino
aster
None/None/1B.2 Cismontane woodland, Coastal scrub,
Lower montane coniferous forest,
Meadows and seeps, Marshes and
swamps, Valley and foothill grassland
(vernally mesic); near ditches, streams,
springs/perennial rhizomatous
herb/July–Nov(Dec)/5–6695
Low potential to occur. Suitable
habitat (coastal scrub and streams)
is present, but the species was not
observed during the focused
special-status plant species surveys
in the Study Area.

Symphyotrichum
greatae
Greata's aster None/None/1B.3 Broadleafed upland forest, Chaparral, Cismontane woodland, Lower montane
coniferous forest, Riparian woodland;
mesic/perennial rhizomatous
herb/June–Oct/980–6595
Low potential to occur. Suitable
habitat riparian woodland) is
present, but the species was not
observed during the focused
special-status plant species surveys
in the Study Area.

Thelypteris
puberula var.
sonorensis
Sonoran
maiden fern
None/None/2B.2 Meadows and seeps (seeps and
streams)/perennial rhizomatous
herb/Jan–Sep/160–2000
Low potential to occur. Suitable
habitat (seeps) is present, but the
species was not observed during
the focused special-status plant
species surveys in the Study Area.

Thysanocarpus
rigidus
rigid fringepod None/None/1B.2 Pinyon and juniper woodland; Dry rocky slopes/annual herb/Feb–
May/1965–7220
Not expected to occur. Suitable
associated habitat is not present in
the Study Area.

Viola pinetorum
ssp. grisea
grey-leaved
violet
None/None/1B.2 Meadows and seeps, Subalpine
coniferous forest, Upper montane
coniferous forest/perennial herb/Apr–
July/4920–11155
Not expected to occur. The Study
Area is outside the elevation range
of the species.

Table Notes:
1 Status abbreviations:

FE: Federally Endangered
FT: Federally Threatened
SE: State Endangered
SR: State Rare
ST: State Threatened
Item #8. Page 596
Meeting Date: 1/24/2023 / Packet Page #: 661
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-10 FEBRUARY 2022
CRPR: California Rare Plant Rank
1A: Plants presumed extirpated in California and either rare or extinct elsewhere 1B: Plants rare, threatened, or endangered in California and elsewhere 2A: Plants presumed extirpated in California but common elsewhere 2B: Plants rare, threatened, or endangered in California but more common elsewhere

Item #8. Page 597
Meeting Date: 1/24/2023 / Packet Page #: 662
APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-11 FEBRUARY 2022
References:

Calflora. 2022. What Grows Here (internet application). Accessed February 2022. https://www.calflora.org/entry/wgh.html CDFW (California Department of Fish and Wildlife). 2014. Endangered Plants - Slender-horned Spineflower. Accessed February 2022. https://www.wildlife.ca.gov/Conservation/Plants/Endangered/Dodecahema-leptoceras CDFW. 2022. California Natural Diversity Database (CNDDB). RareFind 5.0 (Commercial Subscription). Sacramento, California: CDFW, Biogeographic Data Branch. Accessed February 2022. https://nrmsecure.dfg.ca.gov/cnddb/Default.aspx.

California Native Plant Society. 2022. Inventory of Rare and Endangered Plants (online edition, v8-03). Sacramento, California: California Native Plant Society. Accessed February 2022. www.rareplants.cnps.org.

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APPENDIX D. ASSESSMENT OF SPECIAL-STATUS PLANT SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 D-12 FEBRUARY 2022

INTENTIONALLY LEFT BLANK
Item #8. Page 599
Meeting Date: 1/24/2023 / Packet Page #: 664
Appendix E
Assessment of Special-Status Wildlife Species
Potentially Occurring in the Study Area
Item #8. Page 600
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Item #8. Page 601
Meeting Date: 1/24/2023 / Packet Page #: 666
APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-1
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Insects
Euphydryas
editha quino
quino
checkerspot
butterfly
FE/None Annual forblands, grassland, open coastal
scrub and chaparral; often soils with
cryptogamic crusts and fine-textured clay;
host plants include Plantago erecta,
Antirrhinum coulterianum, and Plantago
patagonica
Not expected to occur. Suitable associated
habitat is not present in the Study Area and
the host plants were not observed during the
surveys for the Project.

Fish
Catostomus
santaanae
Santa Ana
sucker
FT/None Small, shallow, cool, clear streams less than
7 meters (23 feet) in width and a few
centimeters to more than a meter (1.5
inches to more than 3 feet) in depth;
substrates are generally coarse gravel,
rubble, and boulder
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Gila orcuttii arroyo chub None/SSC Warm, fluctuating streams with slow-moving or backwater sections of warm to cool
streams at depths >40 centimeters (16
inches); substrates of sand or mud
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Rhinichthys
osculus ssp. 3
Santa Ana
speckled
dace
None/SSC Headwaters of the Santa Ana and San
Gabriel Rivers; may be extirpated from the
Los Angeles River system
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Amphibians
Anaxyrus
californicus
arroyo toad FE/SSC Semi-arid areas near washes, sandy
riverbanks, riparian areas, palm oasis,
Joshua tree, mixed chaparral and sagebrush;
stream channels for breeding (typically third
order); adjacent stream terraces and uplands
for foraging and wintering
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Batrachoseps
gabrieli
San Gabriel
slender
salamander
None/None Talus slopes in forested areas, often near
streams
Not expected to occur. Suitable associated
habitat is not present in the Study Area.

Item #8. Page 602
Meeting Date: 1/24/2023 / Packet Page #: 667
APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-2
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Rana boylii foothill
yellow-legged
frog
None/SSC,
PST
Rocky streams and rivers with open banks in
forest, chaparral, and woodland
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Rana draytonii California
red-legged
frog
FT/SSC Lowland streams, wetlands, riparian
woodlands, livestock ponds; dense, shrubby
or emergent vegetation associated with
deep, still or slow-moving water; uses
adjacent uplands
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Rana muscosa mountain
yellow-legged
frog
FE/SE, WL Lakes, ponds, meadow streams, isolated
pools, and open riverbanks; rocky canyons in
narrow canyons and in chaparral
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Spea
hammondii
western
spadefoot
None/SSC Primarily grassland and vernal pools, but
also in ephemeral wetlands that persist at
least 3 weeks in chaparral, coastal scrub,
valley–foothill woodlands, pastures, and
other agriculture
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Taricha torosa California
newt
None/SSC Wet forests, oak forests, chaparral, and
rolling grassland
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Reptiles
Anniella
stebbinsi
southern
California
legless lizard
None/SSC Coastal dunes, stabilized dunes, beaches,
dry washes, valley–foothill, chaparral, and
scrubs; pine, oak, and riparian woodlands;
associated with sparse vegetation and moist
sandy or loose, loamy soils
Moderate potential to occur. This species
could occur within the coast live oak
woodland, California walnut groves, and
coastal sagebrush scrub habitats within the
Study Area.

Arizona
elegans
occidentalis
California
glossy snake
None/SSC Arid scrub, rocky washes, grasslands,
chaparral. Appears to prefer microhabitats of
open areas and areas with soil loose enough
for easy burrowing.

Low potential to occur. Marginal associated
habitat is present in the Study Area, but there
are few recent records of the species in Los
Angeles County.

Item #8. Page 603
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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-3
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Aspidoscelis
tigris stejnegeri
coastal
whiptail
None/SSC Hot and dry areas with sparse foliage,
including chaparral, woodland, and riparian
areas.

Moderate potential to occur. This species
could occur within the coast live oak
woodland, California walnut groves, and
coastal sagebrush scrub habitats within the
Study Area.

Crotalus ruber red
diamondback
rattlesnake
None/SSC Coastal scrub, chaparral, oak and pine
woodlands, rocky grasslands, cultivated
areas, and desert flats
Not expected to occur. The Study Area is
outside of the range of the species.

Emys
marmorata
western pond
turtle
None/SSC Slow-moving permanent or intermittent
streams, ponds, small lakes, and reservoirs
with emergent basking sites; adjacent
uplands used for nesting and during winter
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Phrynosoma
blainvillii
Blainville's
horned lizard
None/SSC Open areas of sandy soil in valleys, foothills, and semi-arid mountains including coastal
scrub, chaparral, valley–foothill hardwood,
conifer, riparian, pine–cypress, juniper, and
annual grassland habitats
Low potential to occur. While suitable habitat
for the species occurs in the Study, the high
level of human activity has likely negatively
affected the presence of the species in the
area due to direct impacts or the introduction
of non-native ants
Thamnophis
hammondii
two-striped
gartersnake
None/SSC Streams, creeks, pools, streams with rocky
beds, ponds, lakes, vernal pools
Not expected to occur. Suitable associated
aquatic habitat is not present in the Study
Area.

Birds
Athene
cunicularia
(burrow sites &
some wintering
sites)
burrowing
owl
BCC/SSC Nests and forages in grassland, open scrub,
and agriculture, particularly with ground
squirrel burrows
Not expected to occur. Suitable associated
habitat for the species does not occur in the
Study Area or within the immediate vicinity.

Buteo
swainsoni
(nesting)
Swainson's
hawk
BCC/ST Nests in open woodland and savanna,
riparian, and in isolated large trees; forages
in nearby grasslands and agricultural areas
such as wheat and alfalfa fields and pasture
Not expected to occur (nesting). Suitable
associated nesting habitat for the species
does not occur in the Study Area or within the
immediate vicinity. Species may be transient
in the Study Area vicinity during migration.

Item #8. Page 604
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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-4
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Coccyzus
americanus
occidentalis
(nesting)
western
yellow-billed
cuckoo
FT, BCC/SE Inhabits extensive deciduous riparian
thickets or forests, with dense, low-level
understory foliage, and abuts slow-moving
watercourses, backwaters, or seeps; willow
usually a dominant component of the
vegetation; densely foliaged, deciduous trees
and shrubs, especially willows, required for
roosting/nesting sites
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Cypseloides
niger (nesting)
black swift BCC/SSC Nests in moist crevices, caves, and cliffs behind or adjacent to waterfalls in deep
canyons; forages over a wide range of
habitats
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Empidonax
traillii extimus
(nesting)
southwestern
willow
flycatcher
FE/SE Nests in dense riparian habitats along
streams, reservoirs, or wetlands; uses variety
of riparian and shrubland habitats during
migration
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Falco
peregrinus
anatum
(nesting)
American
peregrine
falcon

FDL, BCC/FP,
SDL
Nests on cliffs, buildings, and bridges;
forages in wetlands, riparian, meadows,
croplands, especially where waterfowl are
present
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Icteria virens
(nesting)
yellowbreasted
chat
None/SSC Nests and forages in dense, relatively wide
riparian woodlands and thickets of willows,
vine tangles, and dense brush
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Laterallus
jamaicensis
coturniculus
California
black rail
BCC/FP, ST Tidal marshes, shallow freshwater margins,
wet meadows, and flooded grassy
vegetation; suitable habitats are often
supplied by canal leakage in Sierra Nevada
foothill populations
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Item #8. Page 605
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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-5
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Polioptila
californica
californica
coastal
California
gnatcatcher
FT/SSC Nests and forages in various sage scrub
communities, often dominated by California
sagebrush and buckwheat; generally avoids
nesting in areas with a slope of greater than
40%; majority of nesting at less than 1,000
feet above mean sea level
Not expected to occur. Marginal nesting
habitat for the species does occur in the Study
Area; however, the focused survey for the
species was negative for the Study Area.

Riparia riparia
(nesting)
bank swallow None/ST Nests in riparian, lacustrine, and coastal areas with vertical banks, bluffs, and cliffs
with sandy soils; open country and water
during migration
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Setophaga
petechia
(nesting)
yellow
warbler
None/SSC Riparian plant associations in close proximity to water. Also nests in montane shrubbery in
open conifer forests in Cascades and Sierra
Nevada. Frequently found nesting and
foraging in willow shrubs and thickets, and in
other riparian plants including cottonwoods,
sycamores, ash, and alders.

Present. Observed during the surveys in the
Study Area; however, the species is not
expected to nest in the Study Area due to the
absence of suitable riparian habitat.

Strix
occidentalis
occidentalis
California
spotted owl
BCC/SSC Nests and forages in dense, old-growth,
multi-layered mixed-conifer, redwood, and
Douglas-fir habitats
Not expected to occur. Suitable associated
nesting habitat for the species does not occur
in the Study Area or within the immediate
vicinity.

Vireo bellii
pusillus
(nesting)
least Bell's
vireo
FE/SE Nests and forages in low, dense riparian
thickets along water or along dry parts of
intermittent streams; forages in riparian and
adjacent shrubland late in nesting season
Not expected to occur. Suitable nesting
habitat for the species does occur in the Study
Area; however, the focused survey for the
species was negative for the Study Area.

Mammals
Antrozous
pallidus
pallid bat None/SSC Grasslands, shrublands, woodlands, forests; day roosts are in caves, crevices, mines, and
occasionally in hollow trees and buildings;
night roosts may be in more open sites, such
as porches and open buildings; few
hibernation and maternity sites are known,
but probably uses rock crevices
Low potential to occur. Suitable associated
day/night roosts and foraging habitat for the
individuals of the species occurs within the
Study Area, but hibernation and maternity
sites are not expected to occur.

Item #8. Page 606
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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-6
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Chaetodipus
fallax fallax
northwestern
San Diego
pocket
mouse
None/SSC Coastal scrub, mixed chaparral, sagebrush,
desert wash, desert scrub, desert succulent
shrub, pinyon–juniper, and annual grassland
Not expected to occur. The Study Area is
outside of the range of the species.

Dipodomys
merriami
parvus
San
Bernardino
kangaroo rat
FE/SSC Sparse scrub habitat, alluvial scrub/coastal
scrub habitats on gravelly and sandy soils
near river and stream terraces
Not expected to occur. The Study Area is
outside of the range of the species.

Eumops
perotis
californicus
western
mastiff bat
None/SSC Chaparral, coastal and desert scrub,
coniferous and deciduous forest and
woodland; day and night roosts in crevices in
rocky canyons and cliffs where the canyon or
cliff is vertical or nearly vertical, trees, and
tunnels; nursery roosts described as tight
rock crevices
Low potential to occur. Suitable associated
day/night roosts and foraging habitat for the
individuals of the species occurs within the
Study Area, but hibernation and maternity
sites are not expected to occur.

Lasiurus
cinereus
hoary bat None/None Forest, woodland riparian, and wetland habitats; also juniper scrub, riparian forest,
and desert scrub in arid areas; generally
roosts in dense foliage of medium to large
trees; preferred sites are hidden from above,
with few branches below, and have ground
cover of low reflectivity; females and young
tend to roost at higher sites in trees
Moderate potential to occur. Suitable
associated day/night roosting, maternity
roosts, and foraging habitat for the individuals
of the species occurs within the Study Area,
and there are records of the species from the
San Gabriel Mountains.

Lasiurus
xanthinus
western
yellow bat
None/SSC Valley–foothill riparian, desert riparian,
desert wash, and palm oasis habitats; below
2,000 feet above mean sea level; day/night
roosts in riparian trees and palms; may form
small maternity groups in trees and palms
Low potential to occur. Suitable associated
day/night roosts, maternity roosts, and
foraging habitat for the individuals of the
species occurs within the Study Area; however,
there are few records of the species from the
San Gabriel Mountains.

Lepus
californicus
bennettii
San Diego
black-tailed
jackrabbit
None/SSC Arid habitats with open ground; grasslands,
coastal scrub, agriculture, disturbed areas,
and rangelands
Low potential to occur. Marginal associated
habitat is present in the Study Area.

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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-7
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Microtus
californicus
stephensi
south coast
marsh vole
None/SSC Tidal marshes along the coast Not expected to occur on the Study Area or upstream and downstream from the Study
Area. Suitable associated habitat is not
present in the Study Area, upstream, or
downstream of the Study Area.

Myotis
thysanodes
fringed
myotis
None/None Drier woodlands (oak, pinyon–juniper, and
ponderosa pine), desert scrub, mesic
coniferous forest, grassland, and sage–grass
steppe; sea level to 9,350 feet; roosts in
buildings, mines, rocks, cliff faces, bridges,
and large, decadent trees and snags
Low potential to occur. Suitable associated
day/night roosts and foraging habitat for the
individuals of the species occurs within the
Study Area, but hibernation and maternity
sites are not expected to occur.

Myotis volans long-legged
myotis
None/None Primarily coniferous forests, but also
seasonally in riparian and desert habitats;
roosts in crevices in cliffs, caves, mines,
buildings, exfoliating tree bark, and snags
Low potential to occur. Suitable associated
day/night roosts and foraging habitat for the
individuals of the species occurs within the
Study Area, but maternity roosts habitat is not
present.

Myotis
yumanensis
Yuma myotis None/None Riparian, arid scrublands and deserts, and forests associated with water (streams,
rivers, tinajas); roosts in bridges, buildings,
cliff crevices, caves, mines, and trees
Low potential to occur. Suitable associated
day/night roosts and foraging habitat for the
individuals of the species occurs within the
Study Area, but maternity roosts habitat is not
present.

Neotamias
speciosus
speciosus
lodgepole
chipmunk
None/None Lodgepole pine forests Not expected to occur. The Study Area is outside of the range of the species.

Neotoma
lepida
intermedia
San Diego
desert
woodrat
None/SSC Coastal scrub, desert scrub, chaparral, cacti, rocky areas
Low potential to occur. Marginal habitat is
located within the Study Area, but the species
is expected to occur in the upland areas of the
Arroyo Seco Canyon slopes within rocky areas
or densely vegetated areas.

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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-8
FEBRUARY 2022
Scientific
Name
Common
Name
Status1
(Federal/State) Habitat Potential to Occur
Nyctinomops
femorosaccus
pocketed
free-tailed
bat
None/SSC Pinyon–juniper woodlands, desert scrub,
desert succulent shrub, desert riparian,
desert wash, alkali desert scrub, Joshua tree,
and palm oases; roosts in high cliffs or rock
outcrops with drop-offs, caverns, and
buildings
Low potential to occur. Suitable associated
day/night roosts and foraging habitat for the
individuals of the species occurs within the
Study Area, but maternity roosts habitat is not
present.

Nyctinomops
macrotis
big free-tailed
bat
None/SSC Rocky areas; roosts in caves, holes in trees,
buildings, and crevices on cliffs and rocky
outcrops; forages over water; probably does
not breed in California. In other areas, small
nursery colonies are formed in rocky crevices
in high cliffs.

Low potential to occur. Suitable associated
day/night roosts and foraging habitat for the
individuals of the species occurs within the
Study Area, but maternity roosts habitat is not
present.

Ovis
canadensis
nelsoni
Nelson's
bighorn
sheep
None/FP Steep slopes and cliffs, rough and rocky
topography, sparse vegetation; also canyons,
washes, and alluvial fans
Not expected to occur. Suitable associated
habitat is not present in the Study Area.

Puma concolor cougar None/None Scrubs, chaparral, riparian, woodland, and forest; rests in rocky areas and on cliffs and
ledges that provide cover; most abundant in
riparian areas and brushy stages of most
habitats throughout California, except
deserts
High potential to occur in the study area as a
transient. The species is expected to occur in
the Study Area, specifically the hills southeast
of the project site, as a transient during
foraging, movement through its home range,
or during the dispersal of young; however, the
fences around the property would limit it use
by the species. Natal dens of the species are
not expected since females typically avoid
areas of human activity (Center for Biological
Diversity and the Mountain Lion Foundation
2019).

Taxidea taxus American
badger
None/SSC Dry, open, treeless areas; grasslands, coastal scrub, agriculture, and pastures, especially
with friable soils
Not expected to occur. Suitable associated
habitat is not present in the Study Area and no
diagnostic sign of the species (burrows and
digs) were observed during the surveys.

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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-9
FEBRUARY 2022
Table Notes:
1 Status abbreviations:

FE: Federally Endangered
FT: Federally Threatened
FDL: Federally Delisted
BCC: U.S. Fish and Wildlife Service Bird of Conservation Concern SSC: California Species of Special Concern
FP: California Fully Protected Species
SE: State Endangered
ST: State Threatened
SDL: State Delisted
References:

California Department of Fish and Wildlife. 2019. California Natural Diversity Database (CNDDB). RareFind 5.0 (Commercial Subscription).

Sacramento, California: CDFW, Biogeographic Data Branch. Accessed May 2019. https://nrmsecure.dfg.ca.gov/cnddb/Default.aspx.

Center for Biological Diversity and the Mountain Lion Foundation. 2019. A Petition to List the Southern California/Central Coast Evolutionarily Significant Unit (ESU) of Mountain Lions as Threatened under the California Endangered Species Act (CESA). Accessed January 2021. https://fgc.ca.gov/CESA/index.

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APPENDIX E. ASSESSMENT OF SPECIAL-STATUS WILDLIFE SPECIES POTENTIALLY OCCURRING IN THE STUDY AREA

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 E-10 FEBRUARY 2022

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Item #8. Page 611
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Appendix F
2019 Focused California Gnatcatcher Survey 45-Day
Report for the Grand Estates, City of Glendora, California Item #8. Page 612
Meeting Date: 1/24/2023 / Packet Page #: 677
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August 16, 2019 8375
U.S. Fish and Wildlife Service
Attn: Recovery Permit Coordinator
Carlsbad Fish and Wildlife Office
2177 Salk Avenue, Ste. 250
Carlsbad, CA 92008
Subject: 2019 Focused California Gnatcatcher Survey 45-Day Report for the Silent Ranch Hillside Subdivision Project, City of Glendora, California
Dear Recovery Permit Coordinator:

This report documents the method and results of protocol-level presence/absence surveys conducted for the coastal California gnatcatcher (Polioptila californica californica; CAGN). Focused surveys were conducted throughout all areas of suitable habitat for the proposed Silent Ranch Hillside Subdivision Project located in the City of Glendora, Los Angeles County, California (Attachment A: Figure 1). Suitable habitat for CAGN is approximately

2.84 acres of coastal sage scrub vegetation (Disturbed California sagebrush scrub and disturbed deerweed scrub) within the study area (project site plus a 500-foot buffer). Dudek biologist Tommy Molioo (Authorized Individual under Brock Ortega, TE#813545-8.1) and Melissa Blundell (TE#97717A) conducted CAGN surveys from May through June 2019.

The CAGN is federally-listed as threatened and a California Department of Fish and Wildlife (CDFW) Species of Special Concern. It is closely associated with coastal sage scrub habitat and typically occurs below 950 feet elevation and on slopes less than 40% (Atwood 1990), but CAGN have also been observed at elevations greater than 2,000 feet. The species is primarily threatened by loss, degradation, and fragmentation of coastal sage scrub habitat, and is also impacted by brown-headed cowbird (Molothrus ater) nest parasitism (Braden et al. 1997).

LOCATION AND EXISTING CONDITIONS
The approximately 26.84-acre study area for the project is located within portions of an undeveloped hillside adjacent to an existing residential development in the City of Glendora, Los Angeles County, California (Attachment A: Figure 1). More specifically, the study area is physically located on privately owned land at 950 N. Silent Ranch Dr. The approximate centroid of the study area is at longitude -117.873400° West and latitude 34.152277° North within the U.S. Geological Survey (USGS) 7.5-minute Glendora and Azusa quadrangle maps, Township 10 North, Range 6 West, and Section 4 (USGS 1973). Elevations on site are approximately 1,000 feet to 1,100 feet above mean sea level.

VEGETATION COMMUNITIES
Six vegetation communities and land covers were identified within the study area, which are shown in Figure 2 and tabulated in Table 1. Suitable CAGN habitat within the study area includes disturbed California sagebrush scrub, which is described in detail below.

Item #8. Page 614
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USFWS Recovery Permit Coordinator
Subject: 2019 Focused California Gnatcatcher Survey Report for the Silent Ranch Hillside Subdivision Project 8375
2 August 2019
Table 1
Vegetation Communities and Land Covers within the Study Area Vegetation Community
or Land Cover Map Code Total Study Area (acres)a
Natural Vegetation Communities
California Walnut Grove CWG 0.65
Coast Live Oak Woodland CLOW 8.35
Disturbed California Sagebrush Scrub dCSS 2.84
Non-Natural and Unvegetated Land Covers
California Annual (non-native) Grassland NNG 10.78
Ornamental ORN 2.28
Urban/Developed DEV 1.94
Total 26.84
a Totals may not sum due to rounding.

California Walnut Groves
California walnut groves include California black walnut (Juglans californica) as the dominant or co-dominant tree species in the canopy. This community has a continuous to open canopy less than 15 meters (49 feet) in height with a sparse or grassy ground layer (Sawyer et al. 2009). Species associated with California walnut groves alliance include white alder (Alnus rhombifolia), California ash (Fraxinus dipetala), toyon (Heteromeles arbutifolia), coast live oak (Quercus agrifolia), valley oak (Quercus lobata), arroyo willow (Salix lasiolepis), red willow (Salix laevigata), blue elderberry (Sambucus nigra ssp. caerulea), and California bay (Umbellularia californica) (Sawyer et al. 2009).

California walnut groves on site were burned during the 2014 Colby fire as discussed in Section 2.7. Many of the California walnut trees burned during the fire were observed to be re-sprouting during the 2018 site visit. Several California walnut saplings are emergent throughout canyons and hills within the northern open space portion of the property. One community dominated by California walnut groves is located within the north-central portion of the study area, within the designated open space area. California walnut groves on site are dominated by California black walnut and contain a grassy understory comprised of various bromes (Bromus spp.) and wild oat (Avena spp.).

Other species present include coast live oak, California sycamore (Artemisia californica), Pacific poison oak (Toxicodendron diversilobum), white sage (Salvia apiana), and black mustard (Brassica nigra).

Coast Live Oak Woodland
Coast live oak woodland includes coast live oak as the dominant or co-dominant tree in the canopy. Coast live oak woodland has a continuous to open canopy less than 30 meters (98 feet) in height with a sparse to intermittent shrub canopy and sparse or grassy ground layer (Sawyer et al. 2009). Species associated with the coast live oak woodland alliance include bigleaf maple (Acer macrophyllum), blue oak (Quercus douglasii), box elder (Acer negundo), California bay, Engelmann oak (Quercus engelmannii), California sycamore (Platanus racemosa), southern California black walnut, valley oak, arroyo willow, California black oak (Quercus kelloggii), and madrone (Arbutus menziesii) (Sawyer et al. 2009).

Item #8. Page 615
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USFWS Recovery Permit Coordinator
Subject: 2019 Focused California Gnatcatcher Survey Report for the Silent Ranch Hillside Subdivision Project 8375
3 August 2019
The coast live oak woodlands within the study area are located within the northern portion of the property within areas designated as open space, and along the eastern and western perimeters of the property boundary where development is proposed to occur. The coast live oak woodlands within the northern portion of the property were previously burned during the 2014 Colby fire; however, the community in this portion of the site seems to be recovering well. Coast live oak woodland occurring along the eastern and western boundaries of the property remained untouched by the fire.

This community is dominated by coast live oak, though California sycamore (Platanus racemosa), southern California black walnut, and Washington fan palm (Washingtonia robusta) are also scattered throughout this vegetation community. The understory within the coast live oak woodland mapped within the eastern perimeter of the project site and within the areas zoned as Open Space (north of the project site) include bromes, sowthistles (Sonchus spp.), ragweeds (Ambrosia spp.), Pacific poison oak, tree tobacco (Nicotiana glauca) annual yellow sweetclover (Melilotus indicus), Cucamonga manroot (Marah macrocarpa), Bermuda buttercup (Oxalis pes-caprae), Alefeld’s pea (Lathyrus vestitus var. alefeldii), narrowleaf bedstraw (Galium angustifolium), distant phacelia (Phacelia distans), and wild Canterbury bells (Phacelia minor). The understory within the coast live oak woodland mapped within the western perimeter of the project site is associated with non-native and landscaped species dominated by English ivy (Hedera helix), field bindweed (Convolvulus arvensis), Cucamonga manroot, tree tobacco, ornamental fig trees (Ficus sp.), and Stipa miliaceae.

Disturbed California Sagebrush Scrub
California sagebrush scrub is a community dominated or co-dominated by California sagebrush (Artemisia californica) with a continuous or intermittent shrub canopy less than two meters (seven feet) in height with a variable ground layer (Sawyer et al. 2009). This native plant community characterized by a variety of soft, low, aromatic, drought-deciduous shrubs, such as California sagebrush (Artemisia californica), coyote bush (Baccharis pilularis), Eastern Mojave buckwheat (Eriogonum fasciculatum), brittlebush (Encelia farinosa), chaparral yucca (Hesperoyucca whipplei), coastal prickly pear (Opuntia littoralis), and sages (Salvia spp.), with scattered evergreen shrubs, including lemonadeberry (Rhus integrifolia), laurel sumac (Malosma laurina), and toyon. It typically develops on steep, southfacing slopes and at times, though rarely, occurs on flooded low-gradient deposits along streams in which are scattered willows (Salix spp.) and mulefat (Baccharis salicifolia), depending on the site conditions.

This community was burned during the 2014 Colby fire. Within the project area, this community contains a high cover of non-native species including bromes, wild oat, castor bean (Ricinus communis), and black mustard as a result of the Colby fire. Emergent California sagebrush species including California sagebrush, laurel sumac, white sage, common deerweed have become reestablished. This community previously dominated hillsides throughout the northern open space portion of the study area; however, California sagebrush scrub is now limited as patches along in the eastern portion of the study area.

California Annual (Non-Native) Grassland
California annual grassland (also referred to as non-native grassland in this report) is characterized by a mixture of weedy, introduced annuals, primarily grasses (Sawyer et al. 2009; Holland 1986). California annual grassland typically includes oats, bromes (Bromus diandrus, B. madritensis, B. hordeaceus), black mustard, stork’s bill (Erodium spp.), dove weed (Croton setiger), prickly Russian thistle, and Maltese star-thistle (Centaurea melitensis). It may occur where disturbance by maintenance (e.g., mowing, scraping, disking, and Item #8. Page 616
Meeting Date: 1/24/2023 / Packet Page #: 681
USFWS Recovery Permit Coordinator
Subject: 2019 Focused California Gnatcatcher Survey Report for the Silent Ranch Hillside Subdivision Project 8375
4 August 2019
spraying), grazing, repetitive fire, agriculture, or other mechanical disruption has altered soils and removed native seed sources from areas formerly supporting native vegetation (Holland 1986).

California annual grassland is located throughout the central portion of the study area (within northern portion of where the project development is proposed), as well as within the northern portion of the property within areas zoned as Open Space. This vegetation community is dominated by bromes (Bromus spp.), wild oat (Avena fatua), black mustard, castorbean, redstem stork’s bill (Erodium cicutarium), Cucamonga manroot, and dove weed (Croton setiger).

Other native species found within the eastern portion of this grassland community include sugar sumac (Rhus ovata) and hollyleaf cherry (Prunus ilicifolia ssp. ilicifolia). This area appears to have been heavily altered by regular discing activities. Tree removal activities have also occurred in this area based on past aerial maps of the area. California annual grassland also dominates slopes and ridgelines throughout the northern portion of the study area, within the designated open space. Following the 2014 Colby fire, California annual grassland has re-vegetated hillsides previously dominated by coastal sage scrub communities. A low cover of trees and shrubs remain emergent; however, these hillsides are dominated by bromes, as well as weedy, introduced annuals such as redstem stork’s bill, prickly Russian thistle, and shortpod mustard. Other native species found scattered within this grassland community include laurel sumac, California sagebrush, brittlebush, and California four o’clock (Mirabilis laevis var. crassifolia).

Ornamental
Ornamental plantings refer to areas where non-native ornamentals and landscaping have been installed.

Ornamental planting occur immediately north of West Palm Drive within the southern portion of the study area.

Ornamental species present include Peruvian peppertree, oleander (Nerium oleander), edible fig (Ficus carica), red ironbark (Eucalyptus sideroxylon), olive (Olea europaea), tree of heaven (Ailanthus altissima), Canary Island date palm (Phoenix canariensis), and ornamental pines. Planted natives observed within this land cover include coast live oak, southern California black walnut, and toyon.

Urban/Developed
Developed land refers to areas supporting by man-made structures including homes, yards, roadways, sidewalks, and other highly modified lands supporting structures associated with dwellings or other permanent structures.

Vegetation in these areas, if present at all, is typically associated with development landscaping. Within the study area, developed land is limited to the southwestern portion of the proposed development, consisting of an existing private resident and associated landscaping.

METHODS
The presence/absence focused survey for CAGN was conducted for the project between May 15 and June 28, 2019. The survey was conducted within weather conditions and time frames appropriate for the detection of gnatcatchers. Weather conditions and survey dates are provided below in Table 2. Survey routes are shown in Attachment A: Figure 2. The survey routes focused on moderate to high quality habitat that dominates the majority of the study area. No portions of the survey routes encroached into USFWS designated Critical Habitat for the species.

Item #8. Page 617
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USFWS Recovery Permit Coordinator
Subject: 2019 Focused California Gnatcatcher Survey Report for the Silent Ranch Hillside Subdivision Project 8375
5 August 2019
Table 2 Survey Dates and Conditions
Survey Pass Date Time Personnel1 Weather Conditions
1 May 15, 2019 0800-1030 TM 58°F-62°F, clear skies, 0-1 mph 2 May 22, 2019 0800-1045 TM 55°F-58°F, clear skies, 0-2 mph 3 May 29, 2019 0900-1100 TM 60°F-62°F, clear skies, 0-1 mph 4 June 11, 2019 0830-1030 TM 68°F-75°F, clear skies, 1-2 mph 5 June 21, 2019 0900-1100 MB 70°F-75°F, clear skies, 0-1 mph 6 June 28, 2019 0845-1030 MB 68°F-72°F, clear skies, 1-2 mph 1 Personnel: TM = Tommy Molioo, MB=Melissa Blundell
2 Survey Conditions: °F = degrees Fahrenheit; cc = cloud cover; mph = miles per hour The survey was conducted following the currently accepted protocol of the U.S. Fish and Wildlife Service (USFWS), Coastal California Gnatcatcher (Polioptila californica californica) Presence/Absence Survey Protocol (USFWS 1997). The project site does not occur within an approved NCCP area, and therefore six surveys were conducted at a minimum of 7-day intervals during the breeding season (March 15 through June 30). In accordance with the protocol, no more than 80 acres of suitable habitat were surveyed by a single permitted biologist during each site visit conducted. Survey routes completely covered all areas of suitable CAGN habitat within the survey area and allowed for complete audible and visual coverage of all suitable CAGN habitat on site.

A 200-scale topographic map (1 inch = 200 feet) overlain with vegetation polygons and the survey area was utilized during the survey. Additionally, digital mobile maps were utilized during the surveys to assist in navigating each survey area. Appropriate binoculars (e.g., 8x42 through 10x50 magnification) were used to aid in detecting and identifying bird species. A recording of gnatcatcher vocalizations was played approximately every 50–100 feet to induce responses from potentially present gnatcatchers. Vocalization-playback would have been terminated immediately upon detection of any gnatcatchers to minimize the potential for harassment.

RESULTS
No CAGN (i.e., individuals and/or nests) were detected within the project’s study area in 2019. Therefore, the study area is currently considered absent of CAGN. A full list of bird species observed during the survey and within proximity of the survey area is provided in Attachment B.

I certify that the information in this survey report and attached exhibits fully and accurately represent our work.

Sincerely,
Tommy Molioo
Permit # TE-813545-8.1
Att: A, Figure 1: Project Location
Figure 2: CAGN Survey Map
B, Compendium of Wildlife Species Observed or Detected
Item #8. Page 618
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USFWS Recovery Permit Coordinator
Subject: 2019 Focused California Gnatcatcher Survey Report for the Silent Ranch Hillside Subdivision Project 8375
7 August 2019

REFERENCES
Atwood, J. L. 1990. Status review of the California gnatcatcher (Polioptila californica). Unpublished technical report Manomet Bird Observatory, Manomet, Massachusetts. 79pp.

Braden, G.T, R.L. McKernan, and S.M. Powell. 1997. “Effects of Nest Parasitism by the Brown-Headed Cowbird on Nesting Success of the California gnatcatcher.” Condor 99: 858–865.

CDFW. 2018. "California Natural Community List." Sacramento, California: CDFW. October15, 2018. Accessed July 2019 at https://www.wildlife.ca.gov/Data/VegCAMP/Natural-Communities.

Sawyer, John O., Todd Keeler-Wolf, and Julie Evens. 2009. A Manual of California Vegetation. 2nd ed.

Sacramento, California: California Native Plant Society.

USDA. 2019. Web Soil Survey [web application]. USDA Natural Resources Conservation Service, Soil Survey Staff.

Accessed July 2019. http://websoilsurvey.nrcs.usda.gov/app/ USFWS (U.S. Fish and Wildlife Service). 1997. Coastal California Gnatcatcher (Polioptila californica californica) Presence/Absence Survey Protocol. July 28, 1997.

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Attachment A
Figures
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City of Azusa
City of
Glendora
Project Location
Silent Ranch Hillside Subdivision Project
SOURCE: NAIP 2016
Date: 6/20/2018 - Last saved by: cbattle - Path: Z:\Projects\j837501\MAPDOC\DOCUMENT\BTR\Figure1-ProjectLocation.mxd 0 750 1,500 n Feet
Project Site Boundary
City Limits
FIGURE 1
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Date: 8/14/2019 - Last saved by: cstarbird - Path: Z:\Projects\j837501\MAPDOC\DOCUMENT\FieldMaps\CAGN_FieldMap.mxd CAGN Survey Map
Glendora Hillside Subdivision Project
SOURCE: Bing Maps 2018
0 100 200 n Feet
Project Boundary
CAGN Survey Route
Designated Open Space
Development Area
Dirt Road
Vegetation Communities and Land Covers
CLOW, Coast Live Oak Woodland
CWG, California walnut groves
DEV, Urban/Developed
DEV-CC, Developed-Concrete channel
DH, Disturbed Habitat
EUC, Eucalyptus Woodland
NNG, California annual non-native grassland
ORN, Parks and ornamental plantings
dAcmgla, disturbed Deerweed scrub
dCSS, disturbed California sagebrush scrub
T A G S FIGURE 2
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Item #8. Page 625
Meeting Date: 1/24/2023 / Packet Page #: 690
Attachment B
Compendium of Wildlife Species Observed or Detected
Item #8. Page 626
Meeting Date: 1/24/2023 / Packet Page #: 691
Item #8. Page 627
Meeting Date: 1/24/2023 / Packet Page #: 692
Attachment B
Species Compendium
11830
C-1 July 2019

WILDLIFE
BIRD

BUSHTITS
AEGITHALIDAE—LONG-TAILED TITS & BUSHTITS
Psaltriparus minimus—bushtit

FINCHES
FRINGILLIDAE—FRINGILLINE & CARDUELINE FINCHES & ALLIES
Haemorhous mexicanus—house finch

HUMMINGBIRDS
TROCHILIDAE—HUMMINGBIRDS
Calypte anna—Anna's hummingbird

JAYS, MAGPIES & CROWS
CORVIDAE—CROWS & JAYS
Aphelocoma californica—California scrub-jay
Corvus brachyrhynchos—American crow

MOCKINGBIRDS & THRASHERS
MIMIDAE—MOCKINGBIRDS & THRASHERS
Mimus polyglottos—northern mockingbird

OLD WORLD WARBLERS & GNATCATCHERS
SYLVIIDAE—SYLVIID WARBLERS
Polioptila caerulea—blue-gray gnatcatcher

PIGEONS & DOVES
COLUMBIDAE—PIGEONS & DOVES
Zenaida macroura—mourning dove

WOODPECKERS
Item #8. Page 628
Meeting Date: 1/24/2023 / Packet Page #: 693
Attachment B (Continued)
11830
C-2 July 2019
PICIDAE—WOODPECKERS & ALLIES
Melanerpes formicivorus—acorn woodpecker

NEW WORLD SPARROWS
PASSERELLIDAE—NEW WORLD SPARROWS
Melospiza melodia—song sparrow
Pipilo maculatus—spotted towhee
* signifies introduced (non-native) species
Item #8. Page 629
Meeting Date: 1/24/2023 / Packet Page #: 694
Appendix G
Jurisdictional Delineation Data
Item #8. Page 630
Meeting Date: 1/24/2023 / Packet Page #: 695
Item #8. Page 631
Meeting Date: 1/24/2023 / Packet Page #: 696
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-1
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS01 2 ft A Western Weir
(southeastern extent;
downstream of weir)
Southeast of concrete weir on
the western side of the project
site. Where drainage narrows
into the road. Natural drainage
southeast of downslope of
concrete weir.

Unvegetated, natural bottom Drift and debris
deposits,
exposed roots,
scouring
DS02 22 ft A Western Weir
(southeastern extent;
downstream of weir)
At base, downstream, of
concrete weir, where concrete
lining (apron) is prominent.

Upstream (northwest) of DS01.

Unvegetated, concrete Drift deposits
DS03 26 ft A Western Weir
(southeastern extent)
Concrete weir is filled with rocks
and mesh wiring. USFS 1970
W1. NOTE: "Los Angeles Flood
Control District The function at
this structure is to reduce the
erosion of the stream bed thus
conserving soil and water and
encouraging plant growth. It
was constructed in cooperation
with the United States Forest
Service. For your safety please
stay off."
Unvegetated, concrete. Adjacent
coastal sagebrush (Artemisia
californica; NL; 2%), common
sunflower (Helianthus annuus;
FACU; 5%), and California live
oak (Quercus agrifolia; NL; 20%)
Drift deposits
DS04 21 ft A Western Weir
(southeastern extent;
top of weir)
Northwest and upstream of
concrete weir, natural bottom,
steep slopes.

Natural bottom. California live
oak (Quercus agrifolia; NL;
40%), Eucalyptus (Eucalyptus
sp.; NL; 10%), coastal sagebrush
(Artemisia californica; NL; 2%),
common sunflower (Helianthus
annuus; FACU; 5%), black
mustard (Brassica nigra; NL;
5%), and field bindweed
(Convolvulus arvensis; NL; 1%).

Scouring
Item #8. Page 632
Meeting Date: 1/24/2023 / Packet Page #: 697
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-2
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS05 18 ft A Northwest
(upstream) of
western weir; natural
drainage bottom;
northwest (upstream)
of DS04
Northwest and upstream of
concrete weir, natural bottom,
steep slopes.

Natural bottom. California live
oak (Quercus agrifolia; NL;
40%), Eucalyptus (Eucalyptus
sp.; NL; 10%), coastal sagebrush
(Artemisia californica; NL; 2%),
common sunflower (Helianthus
annuus; FACU; 5%), black
mustard (Brassica nigra; NL;
5%), and field bindweed
(Convolvulus arvensis; NL; 1%).

Scouring
DS06 2 ft A Northwest
(upstream) of
western weir; natural
drainage bottom;
north (upstream) of
DS05
Natural Spring (southern
extent), water flow is present,
though minimal water is
present.

Natural bottom. Edible fig (Ficus
carica; FACU; 10%)
Exposed roots,
scouring
DS07 2 ft A Northwest
(upstream) of
western weir; natural
drainage bottom;
north (upstream) of
DS06
Natural Spring (middle); water
flow is present, though minimal
water is present. Pipe leading to
the southern extent of natural
spring.

Natural bottom. Edible fig (Ficus
carica; FACU; 5%)
Exposed roots,
scouring
DS08 2 ft A Northwest
(upstream) of
western weir; natural
drainage bottom;
north (upstream) of
DS07
Natural Spring (northern
extent); water flow is present,
though minimal water is
present.

Natural bottom. Edible fig (Ficus
carica; FACU; 5%)
Exposed roots,
scouring
Item #8. Page 633
Meeting Date: 1/24/2023 / Packet Page #: 698
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-3
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS09 1 ft B Canyon immediately
east of western weir
(DS01-DS08)
Drainage is not apparent north
of this location (no OHWM).

Drainage flows down the
hillside (steep); however, there
are no OHWM upslope of this
location. First datapoint for
Drainage B was taken here;
where the terrain levels.

Natural bottom. Black mustard
(Brassica nigra; NL; 3%), distant
phacelia (Phacelia distans; OBL;
>1%), Pacific poison oak
(Toxicodendron diversilobum;
NL; 2%), giant wildrye (Elymus
condensatus; NL; 2%), coastal
sagebrush (Artemisia
californica; NL; 2%); leaf litter
(5%).

Exposed roots,
scouring
DS10 3 ft B Canyon immediately
east of western weir;
south (downstream)
of DS09
Downstream (south) of DS09;
where the drainage evens out.

Natural bottom. Black mustard
(Brassica nigra; NL; 3%), Pacific
poison oak (Toxicodendron
diversilobum; NL; 2%),
smilograss (Stipa miliacea; NL;
2%); Barbary fig (Opuntia ficusindica; NL; 1% overstory of California live oak (Quercus
agrifolia; NL; 40%); leaf litter
(5%).

Exposed roots,
scouring
DS11 1 ft B Canyon immediately
east of western weir;
south (downstream)
of DS10
Drainage narrows slightly;
confluence south of DS11.

Natural bottom. Understory
California live oak (Quercus
agrifolia; NL; 5%). Overstory
California live oak (Quercus
agrifolia; NL; 60%)
Scouring
Item #8. Page 634
Meeting Date: 1/24/2023 / Packet Page #: 699
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-4
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS12 2 ft C Canyon immediately
east of Drainage B
(DS09-DS11)
Drainage flows down the
canyon (steep) heading
southward. OHWM not visible
until the terrain levels. There
are visible roots in soil at edge
of bank here.

Natural bottom. Overstory
dominated by Canary Island
date palm (Phoenix canariensis;
NL; 1%), Southern California
black walnut (Juglans
californica; FAC; 2%), edible fig
(Ficus carica; FACU; 1%).

Understory dominated by Pacific
poison oak (Toxicodendron
diversilobum; NL; 2%).

Exposed roots,
scouring
DS13 2 ft C Canyon immediately
east of Drainage B;
upstream of DS12
Drainage flows down the
canyon (steep) heading
southward. OHWM not visible
until the terrain levels. There
are visible roots in soil at edge
of bank here.

Natural bottom. Overstory
California live oak (Quercus
agrifolia; NL; 1%). Leaf litter
(40%).

Exposed roots,
scouring
DS14 1 ft C Canyon immediately
east of Drainage B;
upstream (north) of
DS13
Same drainage narrows
upstream, steep incline in
canyon.

Natural bottom. Black mustard
(Brassica nigra; NL; 3%)
Exposed roots,
scouring
DS15 1 ft C Canyon immediately
east of Drainage B;
upstream (north) of
DS14
Same drainage narrows
upstream, steep incline in
canyon. OHWM not visible
upstream of this point.

Natural bottom. Black mustard
(Brassica nigra; NL; 1%),
Southern California black walnut
(Juglans californica; FAC; 2%),
Pacific poison oak
(Toxicodendron diversilobum;
NL; 1%)
Exposed roots,
scouring
Item #8. Page 635
Meeting Date: 1/24/2023 / Packet Page #: 700
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-5
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS16 1.5 ft D New canyon
immediately east of
Drainage C (DS12-
DS15)
Southern California black
walnut (Juglans californica) in
drainage, slowing the flow of
drainage and creating a clear
OHWM. No OHWM observed
upstream of DS16, canyon is
too steep.

Natural bottom. Back mustard
(Brassica nigra; NL; 1%), laurel
sumac (Malosma laurina; NL;
1%), Southern California black
walnut (Juglans californica; FAC;
5%), Pacific poison oak
(Toxicodendron diversilobum;
NL; 1%)
Exposed roots,
scouring
DS17 1 ft D Same canyon as
above (DS16) but
further downstream
(south) of drainage
Similar to DS16, Southern
California black walnut (Juglans
californica) in drainage, slowing
the flow of drainage and
creating a clear OHWM.

Natural bottom. Black mustard
(Brassica nigra; NL; 1%), laurel
sumac (Malosma laurina; NL;
1%), Southern California black
walnut (Juglans californica; FAC;
1%), Pacific poison oak
(Toxicodendron diversilobum;
NL; 1%)
Exposed roots,
scouring
DS18 2 ft D Same canyon as
above (DS17) but
further downstream
(south) of drainage
This drainage splits into a
braided channel downstream.

Natural bottom. Tree tabacco
(Nicotiana glauca; FAC; 1%),
black mustard (Brassica nigra;
NL; 8%), smilograss (Stipa
miliacea; NL; 2%), distant
phacelia (Phacelia distans; OBL;
>1%), Pacific poison oak
(Toxicodendron diversilobum;
NL; 1%), coastal sagebrush
(Artemisia californica; NL; 2%),
California live oak (Quercus
agrifolia; NL; 5%), Southern
California black walnut (Juglans
californica; FAC; 5%), ripgut
brome (Bromus diandrus; NL;
2%)
Scouring
Item #8. Page 636
Meeting Date: 1/24/2023 / Packet Page #: 701
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-6
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS19 1 ft D Same canyon as
above (DS18) but
further downstream
(south) of drainage
This drainage splits into a
braided channel downstream.

Branches with DS20, below;
eastern portion of channel.

Natural bottom. Blue elderberry
(Sambucus nigra ssp. caerulea;
NL; 10%), Southern California
black walnut (Juglans
californica; FAC; 10%), black
mustard (Brassica nigra; NL;
10%)
Exposed roots,
scouring
DS20 1 ft D Same canyon as
above (DS19) but
further downstream
(south) of drainage
This drainage splits into a
braided channel downstream.

Branches with DS19, above;
western portion of channel.

Natural bottom. Blue elderberry
(Sambucus nigra ssp. caerulea;
NL; 10%), Southern California
black walnut (Juglans
californica; FAC; 10%), black
mustard (Brassica nigra; NL;
10%)
Exposed roots,
scouring
DS21 1 ft D Same canyon as
above, at the
confluence of the two
braided channels
(DS19 and DS20),
just before it meets
with Drainage C
discussed above
Where both braids (DS19 and
DS20) above come together; at
confluence of two canyons
(Drainages C and D). Drainages
flow parallel downslope to
connect into one canyon
(Drainage D)
Natural bottom. Laurel sumac
(Malosma laurina; NL; 10%),
Southern California black walnut
(Juglans californica; FAC; 10%),
Pacific poison oak
(Toxicodendron diversilobum;
NL; 10%)
Exposed roots,
scouring
DS22 3 ft D Same canyon as
above, where
Drainage B meets
Drainages C and D.

At confluence of two canyons
and 3 drainages (B - D).

Natural bottom. Common
sunflower (Helianthus annuus;
FACU; 2%); black mustard
(Brassica nigra; NL; 1%), Canary
Island date palm (Phoenix
canariensis; NL; 5%), tree
tabacco (Nicotiana glauca; FAC;
1%)
Exposed roots,
scouring
Item #8. Page 637
Meeting Date: 1/24/2023 / Packet Page #: 702
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-7
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS23 12 ft D Downstream of the
confluence of the
canyons (Drainages
B-D), immediately
upstream of the
middle concrete weir.

Downstream (south) of
confluence of Drainages B, C,
and D
Natural bottom. Canary Island
date palm (Phoenix canariensis;
NL; 5%), Pacific poison oak
(Toxicodendron diversilobum;
NL; 5%), smilograss (Stipa
miliacea; NL; 2%)
Exposed roots,
scouring
DS24 8 ft D Downstream of the
confluence of the
canyons (Drainages
B-D), immediately
downstream of the
middle concrete weir.

Below concrete weir. Sign
reads,"The function of this
structure is to reduce the
erosion of thestreambed thus
conserving soil and water and
encouraging plant growth, It
was constructed in cooperation
with the United States Forest
Service. For your safety please
keep off."
Natrural bottom. Canary Island
date palm (Phoenix canariensis;
NL; 2%), tree tabacco (Nicotiana
glauca; FAC; 1%), edible fig
(Ficus carica; FACU; 5%), black
mustard (Brassica nigra; NL;
1%), smilograss (Stipa miliacea;
NL; 2%)
Scouring
DS25 3 ft D Downstream of the
confluence of the
canyons (Drainages
B-D), downstream of
the middle concrete
weir.

Drainage confluence of B-D
narrow onto a dirt road and
open area which used to be
coast live oak woodland (CLOW)
and is now non-native
grassland (NNG). Water flows
from western drainage and
follows the northern dirt road
(along retaining wall) through
the site.

Natural bottom. Oleander
(Nerium oleander; NL: 10%)
Scouring
Item #8. Page 638
Meeting Date: 1/24/2023 / Packet Page #: 703
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-8
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS26 N/A Southern
Features
Downstream (south)
of the western weir;
swale/erosional
feature flows from
west to east along a
dirt road into the
center of the project
site. This is the
westernmost data
station point along
this swale/erosion
feature.

The swale/erosional feature
flows from west to east along a
dirt road located at the northern
portion of the project site
(central portion of the study
area). The swale/erosional
feature flows toward the center
of the site.

Unvegetated, natural bottom.

Leaf litter. Overstory California
live oak (Quercus agrifolia; NL;
60%)
Swale/erosional
DS27 N/A Southern
Features
Downstream (south) of
the western weir;
swale/erosional
feature flows from
west to east along a
dirt road into the
center of the project
site; east (downslope)
of DS26.

The swale/erosional feature
flows from west to east along a
dirt road located at the northern
portion of the project site (central
portion of the study area). The
swale/erosional feature flows
toward the center of the site.

Unvegetated, natural bottom.

Leaf litter. Overstory California
live oak (Quercus agrifolia; NL;
60%)
Swale/erosional
DS28 N/A Southern
Features
Downstream (south) of
the western weir;
swale/erosional
feature flows from
west to east along a
dirt road into the
center of the project
site; east (downslope)
of DS27.

The swale/erosional feature
flows from east to west along a
dirt road (same as above). No
herbaceous or shrub layer, just
bare ground and leaf litter.

California live oak (Quercus
agrifolia) overhead. Compacted
soil (along the northern road),
road is rutted out.

Unvegetated, natural bottom.

Leaf litter. Overstory California
live oak (Quercus agrifolia; NL;
60%)
Swale/erosional
Item #8. Page 639
Meeting Date: 1/24/2023 / Packet Page #: 704
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-9
FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS29 N/A Southern
Features
Downstream (south) of
the western weir;
swale/erosional
feature flows from
west to east along a
dirt road into the
center of the project
site; east (downslope)
of DS28.

The swale/erosional feature
flows from east to west along a
dirt road (same as above). No
herbaceous or shrub layer, just
bare ground and leaf litter.

California live oak (Quercus
agrifolia) overhead. Compacted
soil (along the northern road),
road is rutted out.

Unvegetated, natural bottom.

Leaf litter. Overstory California
live oak (Quercus agrifolia; NL;
60%)
Swale/erosional
DS30 N/A Southern
Features
Downstream (south) of
the middle weir (B-D);
swale/erosional
feature is south of the
northern road and
flows into the center of
the site at this
location.

Rocky drop in elevation at a
terraced area that leads into the
center of the site at the
confluence of the channels A-D.

Scouring and erosion has
created a terracing effect which
is from north to south toward the
center of the site.

Swale/erosional feature also
continues east to follow the
northern road into the center of
the site, further east of this
location. Also continues down the
road south and southeast
(addressed later).

Natural bottom. Black mustard
(Brassica nigra; NL; 5%), tree
tobacco (Nicotiana glauca; FAC;
3%), ripgut brome (Bromus
diandrus; NL; 2%)
Swale/erosional
DS31 N/A Southern
Features
Downstream (south) of
the middle weir (B-D);
swale/erosional feature
is south of the northern
road into the center of
the site; south
(downstream) of DS30.

Downstream of DS30 along the
western fork of the feature. Some
scouring is visible then it tapers
off into a low point on the
property sheet flow. This fork of
the feature ends at this point.

Natural bottom. Castorbean
(Ricinus communis; FACU; 5%),
ripgut brome (Bromus diandrus;
NL; 5%), smilograss (Stipa
miliacea; NL; 2%)
Swale/erosional
Item #8. Page 640
Meeting Date: 1/24/2023 / Packet Page #: 705
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-10 FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS32 N/A Southern
Features
Downstream (south)
of the middle weir (BD); swale/erosional
feature is south of
the northern road
into the center of the
site; south
(downstream) of
DS30.

Downstream of DS30 along the
middle fork of the feature,
parallel with DS31 and DS33.

Some scouring is visible then it
tapers off into a low point on
the property sheet flow. This
fork of the drainage ends at this
point.

Natural bottom. Black mustard
(Brassica nigra; NL; 8%), distant
phacelia (Phacelia distans; OBL;
2%), Maltese star-thistle
(Centaurea melitensis; NL; 1%),
mat amaranth (Amaranthus
blitoides; FACW; 2%), tree
tobacco (Nicotiana glauca; FAC;
5%)
Swale/erosional
DS33 N/A Southern
Features
Downstream (south)
of the middle weir (BD); swale/erosional
feature is south of
the northern road
into the center of the
site; south
(downstream) of
DS30.

Downstream (south) of DS30
along the easternmost fork of
the feature, parallel with DS31
and DS32. Continues further
downstream to DS34.

Natural bottom. Black mustard
(Brassica nigra; NL; 10%)
Swale/erosional
DS34 N/A Southern
Features
Downstream (south)
of the middle weir (BD); swale/erosional
feature is south of
the northern road
into the center of the
site; downstream
(south) of DS33.

Downstream (south) of DS33
(DS33 continues here). DS34
continues through the center of
the site.

Natural bottom. Black mustard
(Brassica nigra; NL; 10%), tree
tobacco (Nicotiana glauca; FAC;
5%)
Swale/erosional
DS35
(line)
N/A Southern
Features
Swale/erosional
feature is through
the center of the site
and follows the dirt
road south into the
arizona crossing at
the southern end of
the site (entryway)
Swale/erosional feature is
through the property and
eventually down the dirt road.

Natural bottom. Ripgut brome
(Bromus diandrus; NL; 30%),
tree tabacco (Nicotiana glauca;
FAC; 2%), black mustard
(Brassica nigra; NL; 35%),
Canary Island date palm
(Phoenix canariensis; NL; 2%)
Swale/erosional
Item #8. Page 641
Meeting Date: 1/24/2023 / Packet Page #: 706
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-11 FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS36-40
(line)
N/A Southern
Features
Swale/erosional
feature is through
the center of the site
and follows the dirt
road south into the
arizona crossing at
the southern end of
the site (entryway)
Swale/erosional feature is
through the property and down
the dirt road (along the western
side of the road then to the
eastern side of the road). Looks
like road ruts. Took a line point
to illustrate this feature.

Swale/erosional feature is
towards southeast corner of
project site.

Natural bottom. Very limited veg,
compacted soil (dirt road).

Swale/erosional
DS41 N/A Southern
Features
Swale/erosional
feature is east of the
road and drainage AD above (DS35-40
above)
Swale/erosional feature is
through the property and down
the site with ornamental veg.

Swale/erosional feature is
north to south, east of the road
and Southern Features.

Natural bottom. Ornamental
trees in general area
surrounding drainage. Black
mustard (Brassica nigra; NL;
10%), olive (Olea europaea; NL;
5%), Maltese star-thistle
(Centaurea melitensis; NL; 1%),
ripgut brome (Bromus diandrus;
NL; 5%), glodentop grass
(Lamarckia aurea; FACU; 2%),
compact brome (Bromus
madritensis; UPL; 3%).

Swale/erosional
DS42 3 ft E Upstream of
easternmost
weir/drainage; east
of Drainages B-D.

Exposed root hairs in drianage,
intact soil layer, upstream the
erosion is more prominent and
then it fades out.

Natural bottom. Edible fig (Ficus
carica; FACU; 25%), tree tobacco
(Nicotiana glauca; FAC; 1%),
Pacific poison oak
(Toxicodendron diversilobum;
NL; 1%)
Exposed roots,
scouring
Item #8. Page 642
Meeting Date: 1/24/2023 / Packet Page #: 707
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-12 FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS43 6 ft E Upstream of
easternmost
weir/drainage; south
(downstream) of
DS42.

Exposed root hairs in drianage,
intact soil layer, upstream the
erosion is more prominent and
then it fades out.

Natural bottom. Edible fig (Ficus
carica; FACU; 2%), Canary Island
date palm (Phoenix canariensis;
NL; 2%), California live oak
(Quercus agrifolia; NL; 5%), tree
tobacco (Nicotiana glauca; FAC;
1%), California sycamore
(Platanus racemosa; FAC; 5%)
Exposed roots,
scouring
DS44 12 ft E Upstream of
easternmost
weir/drainage; south
(downstream) of
DS43.

Exposed root hairs in drianage,
intact soil layer, upstream the
erosion is more prominent and
then it fades out.

Natural bottom. Overstory edible
fig (Ficus carica; FACU; 10%),
Califonia sycamore (Platanus
racemosa; FAC; 20%), California
live oak (Quercus agrifolia; NL;
20%)
Exposed roots,
scouring
DS45 14 ft E Upstream of
easternmost
weir/drainage; south
(downstream) of
DS44.

Exposed root hairs in drianage,
intact soil layer
Natural bottom. Black mustard
(Brassica nigra; NL; 1%), edible
fig (Ficus carica; FACU; 5%),
California live oak (Quercus
agrifolia; NL; 5%)
Exposed roots,
scouring
DS46 2 ft E Upstream of
easternmost
weir/drainage; south
(downstream) of
DS45.

Exposed root hairs in drianage,
intact soil layer
Natual bottom. California live
oak (Quercus agrifolia; NL;
10%); Southern California black
walnut (Juglans californica; FAC;
10%)
Exposed roots,
scouring
DS47 3.5 ft E Upstream of
easternmost
weir/drainage; south
(downstream) of
DS46.

Exposed root hairs in drianage,
intact soil layer
Natual bottom. California live
oak (Quercus agrifolia; NL;
10%); Southern California black
walnut (Juglans californica; FAC;
10%)
Exposed roots,
scouring
DS48 No
visible
OHWM
E Upstream of
easternmost
weir/drainage; south
(downstream) of
DS47.

Exposed root hairs in drianage,
intact soil layer
Natural bottom. Common
sunflower (Helianthus annuus;
FACU; 20%), Califonia sycamore
(Platanus racemosa; FAC; 20%)
Exposed roots,
scouring
Item #8. Page 643
Meeting Date: 1/24/2023 / Packet Page #: 708
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-13 FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS49 No
visible
OHWM
E Upstream of
easternmost
weir/drainage; south
(downstream) of
DS48.

Exposed root hairs in drianage,
intact soil layer
Natural bottom. Overstory
California live oak (Quercus
agrifolia; NL; 50%). Understory
common sunflower (Helianthus
annuus; FACU; 20%), hollowleaf
annual lupine (Lupinus
succulentus; NL; 10%), distant
phacelia (Phacelia distans; OBL;
1%), black mustard (Brassica
nigra; NL; 10%), Chilean bird’sfoot trefoil (Acmispon
wrangelianus; NL; 10%)
Exposed roots,
scouring
DS50 25 ft E At the Easternmost
Concrete Weir; south
(downstream) of
DS49.

Concrete weir is filled with rocks
and mesh wiring.

Concrete bottom of weir.

Adjacent overstory California live
oak (Quercus agrifolia; NL;
50%). Understory castorbean
(Ricinus communis; FACU; 40%),
common sunflower (Helianthus
annuus; FACU; 5%), distant
phacelia (Phacelia distans; OBL;
1%), black mustard (Brassica
nigra; NL; 10%), Chilean bird’sfoot trefoil (Acmispon
wrangelianus; NL; 10%)
Drift deposits
DS51 23 ft E Concrete area,
downstream (south)
of the easternmost
weir (DS50).

Concrete apron with cracks.

Vegetation growing through
cracks and adjacent to
concrete.

Natural bottom. Canary Island
date palm (Phoenix canariensis;
NL; 5%), California live oak
(Quercus agrifolia; NL; 10%),
olive (Olea europaea; NL; 15%).

Understory smilograss (Stipa
miliacea; NL; 2%)
Drift deposits
Item #8. Page 644
Meeting Date: 1/24/2023 / Packet Page #: 709
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-14 FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS52 5 ft E Concrete channel
conveys water along
the eastern side of
the site; downstream
(south) of concrete
weir and DS51.
no vegetation within concrete
drain (concrete basin), some
leaf litter; no adjacent riparian
vegetation
Concrete bottom. No vegetation. Trapezoidal
concrete
channel
DS53 5 ft E Concrete channel
conveys water along
the eastern side of
the site; downstream
(south) of concrete
weir.
no vegetation within concrete
drain (concrete basin), some
leaf litter; no adjacent riparian
vegetation
Concrete bottom. No vegetation. Trapezoidal
concrete
channel
DS54 4 ft E Concrete channel
conveys water along
the eastern side of
the site; downstream
(south) of concrete
weir.
no vegetation within concrete
drain (concrete basin), some
leaf litter; no adjacent riparian
vegetation
Concrete bottom. No vegetation. Trapezoidal
concrete
channel
DS55-56 5 ft E Concrete channel
conveys water along
the eastern side of
the site; downstream
(south) of concrete
weir (southern
portion of the site).
no vegetation within concrete
drain (concrete basin), some
leaf litter; no adjacent riparian
vegetation. Pruili observed
along the concrete basin
towards the southern portion of
the site
Concrete bottom. No vegetation. Trapezoidal
concrete
channel
DS57 12 ft
(arizona
crossing
base)
E Water flows from the
middle drainage
down the road to
meet up with the
concrete basin along
the southern portion
of the site
Dirt road, no vegetation, bare
compacted ground. Concrete
portions with no vegetation.

Concrete bottom. No vegetation. Arizona crossing
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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-15 FEBRUARY 2022
Data
Station
(DS) No. OHWM
Feature
Name General Area Notes Vegetation Hydrology
DS58 1 ft Southern
Features
Eastern portion of
the dirt road through
the center of the site
(east of DS30 -
DS34).

Dirt road, no vegetation, bare
compacted ground.

Natural bottom. No vegetation. Swale/erosional
DS59 1 ft Southern
Features
Eastern portion of
the dirt road through
the center of the site
(east of DS30 -
DS34).

No vegetation, bare ground. Dirt
road is compacted.

Natural bottom. No vegetation. Swale/erosional
Legend:

NL = not listed
OBL = obligate wetland species
FACU = facultative upland species
FAC = facultative wetland species
FAC = facultative species
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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-16 FEBRUARY 2022
Overview of eastern portion of the site, southwest
of DS52, facing northeast.

Overview of asphalt storage area south of DS01,
facing northwest.

Asphalt storage area southeast of Drainage A. Data Station (DS) 01. Drainage A facing north, upstream.

Item #8. Page 647
Meeting Date: 1/24/2023 / Packet Page #: 712
APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-17 FEBRUARY 2022
DS02. Drainage A facing northeast. DS03. Drainage A concrete weir facing northwest, upstream.

Placard on Drainage A concrete weir. DS03. Drainage A concrete weir facing southeast, downstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-18 FEBRUARY 2022
DS04. Drainage A facing northwest, upstream. DS06. Drainage A facing northwest, upstream.

Natural spring.

DS07. Drainage A facing northwest, upstream.

Natural spring.

DS08. Drainage A facing southeast, downstream.

Natural spring.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-19 FEBRUARY 2022
Overview of Drainage A facing southwest. DS09. Drainage B facing northwest, upstream. 072 DS10. Drainage B facing northwest, upstream. DS11. Drainage B facing southeast, downstream.

Item #8. Page 650
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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-20 FEBRUARY 2022
Overview of Drainage B facing northwest,
upstream.

DS12. Drainage C facing southeast, downstream.

DS13. Drainage C facing northwest, upstream. DS14. Drainage C facing northwest, upstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-21 FEBRUARY 2022
DS15. Drainage C facing northwest, upstream. DS16. Drainage D facing northeast, upstream.

DS16. Drainage D close-up of scouring and
exposed roots.

DS17. Drainage D facing northeast, upstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-22 FEBRUARY 2022
DS18. Drainage D facing southwest, downstream. DS19. Drainage D facing southwest, downstream.

DS20. Drainage D facing north, upstream. DS21. Confluence of Drainage C, on the left, and Drainage D, on the right, facing north, upstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-23 FEBRUARY 2022
DS22. Confluence of Drainage B, on the left, and
Drainage C/D, on the right, facing upstream.

DS23. Downstream of confluence of Drainage B, C,
and D facing north, upstream.

DS24. Downstream of confluence of Drainage B, C,
and D at concrete weir facing north.

DS25. Downstream of confluence of Drainage B, C,
and D facing north, upstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-24 FEBRUARY 2022
DS26. Swale/Erosional Features facing
east, downstream.

DS27. Swale/Erosional Features facing
west, upstream.

DS28. Swale/Erosional Features facing
east, downstream.

DS29. Swale/Erosional Features facing
west, upstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-25 FEBRUARY 2022
DS30. Overview of Swale/Erosional Features facing southeast.

DS31. Swale/Erosional Features, western drainage
downstream of DS30, facing north, upstream.

DS32. Swale/Erosional Features, central drainage
downstream DS30, facing south, downstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-26 FEBRUARY 2022
DS33. Swale/Erosional Features, eastern drainage
downstream of DS30, facing north, upstream.

DS34. Swale/Erosional Features, downstream
eastern drainage, facing south, downstream.

DS35. Swale/Erosional Features facing
south, downstream.

DS36-DS40. Swale/Erosional Features along edge
of dirt roads facing north, upstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-27 FEBRUARY 2022
DS36-DS40. Swale/Erosional Features along edge
of dirt roads facing southeast, downstream.

DS36-DS40. Swale/Erosional Features along edge
of dirt roads facing southeast, downstream.

DS36-DS40. Swale/Erosional Features along edge
of dirt roads facing northwest, upstream.

DS36-DS40. Swale/Erosional Features along edge
of dirt roads facing southeast, downstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-28 FEBRUARY 2022
DS41. Swale/Erosional Features east of DS36-40,
also through the center of the site; facing
southeast, downstream.

DS42. Drainage E facing southeast, downstream.

DS43. Drainage E facing south, downstream. DS44. Drainage E facing south, downstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-29 FEBRUARY 2022
DS45. Drainage E facing south, downstream. DS46. Drainage E facing south, downstream.

DS47. Drainage E facing south, downstream. DS48. Drainage E facing south, downstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-30 FEBRUARY 2022
DS49. Drainage E facing north, upstream. DS49. Drainage E facing south, downstream.

DS50. Drainage E concrete weir facing
north, upstream.

DS51. Drainage E concrete weir facing
north, upstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-31 FEBRUARY 2022
DS52. Drainage E facing north, upstream. DS53. Drainage E facing south, downstream.

DS54. Drainage E facing north, upstream. DS55. Drainage E facing south, downstream.

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APPENDIX G. JURISDICTIONAL DELINEATION NOTES

GRAND ESTATES PROJECT / BIOLOGICAL RESOURCES TECHNICAL REPORT 8375 G-32 FEBRUARY 2022
DS56. Drainage E at outfall Palm Drive and Grand
Avenue facing south, downstream.

DS57. Drainage E Arizona crossing facing
west, upstream.

DS58. Swale/Erosional Features facing
south, downstream.

DS59. Swale/Erosional Features facing
south, downstream.

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Appendix H
Tree Information Matrix (2020), Tree Locations (2020),
and Initial Tree Report (2019)
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Item #8. Page 665
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Tree Report
For
Glendora Heights
Prepared by
Robert T. Bennett
ISA Certified Arborist #WE-3724AT
California Landscape Contractors License #796645
ISA Tree Risk Assessment Qualified
402 E. Plymouth St
Glendora, California 91740
Cell #626-991-2376
Date: September 15, 2018
Revised : August 24, 2019
Item #8. Page 666
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August 24, 2019
2 Contents
Location………………………………………………………………..

Site conditions…………………………………………..………….....

I. Objective………………………………..……………………...

II. Methods of Tree Analysis…………………………………….

III. Tree Identification……………………………………………..

IV. Results of Tree Evaluation…….……………………………..

V. Result of Field Analysis…………………..…………………..

VI. Summary of Field Analysis…………………………………..

VII. Recommendations……………………………………………
Definitions of Tree Evaluation Terms

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August 24, 2019
3 Site Location
Phase 1
The site is located at the north end of Grand Ave in the city of Glendora California.

Phase 2
This area is above the Glendora Heights project. The property line of the project runs in an EastWest direction along the base of the hill.

Site Conditions
Phase 1
The property was planted with many non-native trees as well as native oaks and sycamores. None of the trees appeared to have ever been pruned.

The Beefwood trees exhibited very poor structure and form with broken branch wounds throughout the canopies.

The majority of Canary Island Pines were planted in a large grouping. These trees have depended upon each other for support during wind events. Many of the oaks on the Northwest section of the property as well as the Pines and Eucalyptus trees were removed and used for firewood.

The Colby fire burned through the oak woodland in the northeast portion of the property damaging many of the trees. Fire crews removed trees on the perimeter during the fire.

The majority of the trees are showing signs of drought stress.

Phase 2
There ae three neglected debris basins constructed in the late 1960’s or early 1970’s to control the debris that has washed down in the past 48 years.

At the time of the construction of the debris basins care was not taken to prevent the loss of oak trees. As the basins filled up with sand and debris, the roots and trunks of the existing Oaks were covered and the grades were raised to the detriment of the trees. Many trees have died due to the grade changes.

Fire has had a devastating effect on the health of the trees. Without mans’ intervention most of the trees will slowly recover while many will succumb to their injuries. This will take many years to Item #8. Page 668
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4 ascertain. Some trees were removed in early 2014 because they were not protected as they were non-native trees on private property.

I. Objectives
The objective of this report is to locate, record and evaluate all trees that will or may be impacted by the construction project. This information will assist the city staff in calculating the number of trees to be mitigated by tree replacement. Trees identified on a site map provided by the engineering firm.

The trees will be evaluated for health, disease, pests, structural defects, fire damage, and vigor.

The physical characteristics of the trees will be recorded including height, DBH and distance to the drip line (root protection zone).

II. Methods of Tree Analysis
I, Robert T Bennett, on August 15, 2019 performed a visual inspection and assessment of the trees. • All trees within the area that were delineated by the plans were tagged with metal 1 ¼ inch tags placed on the trunk in a conspicuous position so they can be spotted easily from a distance.
• The trees were measured with a diameter tape developed for this purpose. • The trees were evaluated for physical structure, species, disease, pests and health.

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August 24, 2019
5 III. Tree Identification
List of Trees:

Native
• California Black Walnut (Juglans
californica)
• California Sycamore (Platanus
racemosa)
• Coast Live Oak (Quercus agrifolia)
• Douglas Fir (Pseudotsuga macrocarpa)
• Toyon (Heteromeles arbutifolia)
Non-Native
• Beefwood (Casuarina Beefwood)
• Bunya Bunya (Araucaria bidwillii)
• Canary Island Date Palm (Phoenix canariensis)
• Canary Island Pine (Pinus canariensis)
• Deodar Cedar (Cedrus deodara)
•Douglas Fir (Pseudotsuga macrocarpa)
• English Walnut (Juglans regia)
• Italian Stone Pine (Pinus pinea)
• Jacaranda (Jacaranda mimosifolia)
• Mexican Fan Palm (Washingtonia
robusta)
• Olive (Olea europaea) •
• Plum (Prunus sap) •
• Red Iron Bark (Eucalyptus sideroxylon)
• Silk Oak (Grevillea robusta)

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August 24, 2019
6 V. Results of Field Evaluation
Tree evaluation forms are provided with the report. The following information is in addition to tree evaluation forms:

1. Tree Numbers/Description of Health
VI. Summary of Field Evaluation
My original arborist report for this project was completed in February 2014. The Colby fire occurred during this time. Many trees were evaluated prior to the fire and others were evaluated after the fire.

A large number of the trees including the native oaks were damaged by the fire have succumbed to their injuries in the 41/2 years since the fire.

The report for this project was required by the City of Glendora Planning Department staff and since the tree ordinance had been updated, more trees were added to the report.

The total number of trees on this report is approximately 600.

This report is divided in 2 sections:

Section/Phase 1 contains 266 trees in the updated original report.

Section/Phase 2 contains 330 trees which is the added requirement to evaluate for the flood control area above the original project.

Revision added to Section/Phase 2 on August 24, 2019
As of August 24, 2019 I reviewed and updated the Preliminary Site Development plan submitted as requested. The plan included a larger area of grading higher up on the slopes than originally required due to the increased flood control requirements of the project.

When I completed my Tree Evaluations of the original Phase 2 area, I had already included all of the trees up the slope to the tree line. The tree line is the point where trees of a qualifying size (6 inches Item #8. Page 671
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August 24, 2019
7 DBH) have stopped growing. Above this line the vegetation changes to small chaparral plants and grasses. Many of the trees documented in my original phase 2 report were outside of the area at that time, however they are now included per the revised map that was approved on April 4, 2019 by the City of Glendora which included a larger area for the Flood Control area as required by Los Angeles Flood Control District on this map.

2. Section/Phase 1 – Original Arborist in February 2014 The Canary Island Pines have grown depending upon each other for support during wind events.

These pines should not be left individually in a landscape because they may be subject to wind throw.

The Beefwood trees are all poor candidates to be retained in a new landscape. These trees have grown adjacent to the stand of Canary Pines and have benefited from the wind protection they provided. The tall thin trees may have branch failure during wind events if the stand of trees is thinned.

The Mexican Fan Palms are very tall and are unable to be relocated and supported. The Canary Palm would be good candidates for relocation.

The Colby fire will need time to recover to determine the extent of the damage to the individual trees in the woodland.

The trees on this property have been ravaged by neglect, drought, fire, and firewood collection.

During the Colby fire, firefighters fell dozens of trees intending to halt the advance of the fire by creating a fire break. Most of these trees were non-native species (Pine, Eucalyptus and Olives) and most of the felled wood was gathered and used for firewood. As noted on my tree evaluation forms, many trees have succumbed to the drought.

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August 24, 2019
8 3. Section/Phase 2 – Updated Requirements
The second half of the report is focused on the hillside and debris basins to the north of the proposed housing project. This area above the project has had debris basins constructed in the late 1960’s and 1970’s to contain the debris after the devastating fires and floods. The basins are now full and no longer functional as designed.

The preliminary plans called for cleanout of the basins and grading and cleaning of the hillside surrounding the structures. In this report, trees numbered 270 through 600 are located, measured and evaluated in this area.

Many of the oaks are just now 4.5 years after the fire and are suffering catastrophic failure due to that fire that went through the property. Fire damage to trees takes years to manifest with native wood decay, pathogens and insects to degrade the structural integrity of the tree causing catastrophic failure of branches and trunks of trees. Dead trees in the bottom of the debris basin have died to the grade being raised around them along with drought and fire. The majority have failed at the soil level and all are decayed.

VIII. Recommendations
All of the non-native trees have grown for many, many years without proper pruning and care.

The Canary Pines have grown dependent on each other for support from the winds, for these reasons removing trees and leaving individual trees standing in a new landscape may create a condition where the remaining trees could fail in the case of a significant weather incident.

Creating hazardous conditions in a new landscape should be avoided at all costs.

Therefore I recommend that all of the non-native trees be removed.

The Canary Palms may be moved unless they can be incorporated into the new properties.

The majority of the trees in the Northeast corner of this phase have suffered catastrophic damage because of the fire. Now, after almost 5 years the effects of the fire are becoming evident. Total failure of main trunks is common as well as cavities forming and massive branch die-back.

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August 24, 2019
9 Many of the trees throughout this project are in the same condition due to drought and fire damage.

The extreme poor health of the trees should be considered by the city when calculating tree replacement values.

A grading and construction plan for the rejuvenation of the three debris basins and the surrounding hillsides will be provided by Giron Engineering.
• IF all the trees in this planned area and debris basin restructuring are to be removed, here are the number of replacement trees per Glendora City Ordinance (page 21).

Oaks All Other Species

1. 36” Box = 365 1. 24” Box = 84

2.48” Box = 405 2. 36” Box = 115

3. 48” Box = 11
• Tree replacement to be determined by the City Forester over 37” DBH Oaks All Other Species

1. 7 trees 1. 0 trees
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Tree Locations
Silent Ranch Hillside Subdivision Project
SOURCE: County of Los Angeles 2018; Bing Maps 2018; NHD 2018 0 30 60Feet

SHEET A
CloverviewDr
W Palm Dr
Sheet E
Sheet D
Sheet A Sheet B
Sheet C
Tree Locations
California sycamore (Platanus racemosa)
Mexican fan palm (Washingtonia robusta)
Southern California black walnut (Juglans californica)
coast live oak (Quercus agrifolia)
fruitless olive (Olea europaea)
spotted gum (Corymbia maculata)
swamp mahogany (Eucalyptus robusta)
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Tree Locations
Silent Ranch Hillside Subdivision Project
SOURCE: County of Los Angeles 2018; Bing Maps 2018; NHD 2018 0 30 60Feet

SHEET B
CloverviewDr
W Palm Dr
Sheet E
Sheet D
Sheet A Sheet B
Sheet C
Tree Locations
California sycamore (Platanus racemosa)
Canary Island date palm (Phoenix canariensis)
Mexican fan palm (Washingtonia robusta)
Southern California black walnut (Juglans californica)
coast live oak (Quercus agrifolia)
fruitless olive (Olea europaea)
jacaranda (Jacaranda mimosifolia)
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Residence
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Tree Locations
Silent Ranch Hillside Subdivision Project
SOURCE: County of Los Angeles 2018; Bing Maps 2018; NHD 2018 0 30 60Feet

SHEET C
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Tree Locations
Brazilian pepper (Schinus terebinthifolia)
California sycamore (Platanus racemosa)
Canary Island pine (Pinus canariensis)
English walnut (Juglans regia)
Italian stone pine (Pinus pinea)
Mexican fan palm (Washingtonia robusta)
Peruvian pepper (Schinus molle)
Southern California black walnut (Juglans californica)
Victorian box (Pittosporum undulatum) blue atlas cedar (Cedrus atlantica 'glauca') citrus tree (Citrus spp.)
coast live oak (Quercus agrifolia)
fruiting plum (Prunus domestica)
fruitless olive (Olea europaea)
spotted gum (Corymbia maculata)
strawberry madrone (Arbutus unedo)
swamp mahogany (Eucalyptus robusta)
toyon (Heteromeles arbutifolia)
weeping fig (Ficus benjamina)
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Tree Locations
Silent Ranch Hillside Subdivision Project
SOURCE: County of Los Angeles 2018; Bing Maps 2018; NHD 2018 0 30 60Feet

SHEET D
CloverviewDr
W Palm Dr
Sheet E
Sheet D
Sheet A Sheet B
Sheet C
Tree Locations
Unknown Species
American elderberry (Sambucus canadensis)
California sycamore (Platanus racemosa)
California sycamore (Platauna racemosa)
Canary Island date palm (Phoenix canariensis)
Canary Island pine (Pinus canariensis)
Douglas-fir (Pseudotsaya menziesii)
English walnut (Juglans regia)
Mexican fan palm (Washingtonia robusta)
Peruvian pepper (Schinus molle)
Southern California black walnut (Juglans californica)
bunya-bunya (Arucaria bidwillii)
carob (Ceratonia siliqua)
carob tree (Ceratonia siliqua)
coast live oak (Quercus agrifolia)
deodar cedar (Cedrus deodora)
fruitless olive (Olea europaea)
jacaranda (Jacaranda mimosifolia)
river she-oak (Casuarina cunninghamiana)
rubber tree (Ficus elastica)
silk oak (Grevillea robusta)
sugar gum (Eucalyptus cladocalx)
swamp mahogany (Eucalyptus robusta)
swamp mahogny (Eucalyptus robusta)
toyon (Heteromeles arbutifolia)
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W Palm Dr
Cloverview Dr
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Tree Locations
Silent Ranch Hillside Subdivision Project
SOURCE: County of Los Angeles 2018; Bing Maps 2018; NHD 2018 0 30 60Feet

SHEET E
C
l
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v
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W Palm Dr
Sheet E
Sheet D
Sheet A Sheet B
Sheet C
Tree Locations
California sycamore (Platanus racemosa)
Canary Island date palm (Phoenix canariensis)
Canary Island pine (Pinus canariensis)
Mexican fan palm (Washingtonia robusta)
coast live oak (Quercus agrifolia)
deodar cedar (Cedrus deodora)
fruitless olive (Olea europaea)
jacaranda (Jacaranda mimosifolia)
river she-oak (Casuarina cunninghamiana)
silk oak (Grevillea robusta)
silk oak (Grevillea robusta)
toyon (Heteromeles arbutifolia)
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Tree
No.

Botanical Name Common Name Protected Diameter at Standard Height (inches) Stems Stem 1 Stem 2 Stem 3 Stem 4 Stem 5 Height (Feet) Width
(Feet) Health Structure Notes Lat. Long.
1 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 22 25 Fair Poor tree is topped, growing under
power lines 34.150459 -117.872638
2 Casuarina
cunninghamiana river she-oak No 7 1 7 0 0 0 0 22 12 Good Good 34.150423 -117.872667 3 Casuarina
cunninghamiana river she-oak Yes 29 1 29 0 0 0 0 60 20 Good Good 34.150417 -117.87273 4 Pinus canariensis Canary Island pine Yes 26 1 26 0 0 0 0 70 20 Good Poor 34.150429 -117.872762 5 Jacaranda mimosifolia jacaranda Yes 20 3 10 5 5 0 0 18 18 Fair Poor tree is topped, growing under
power lines 34.15048 -117.872633
6 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 90 15 Good Fair 34.150509 -117.872972 7 Pinus canariensis Canary Island pine Yes 30 1 30 0 0 0 0 90 30 Good Fair 34.150649 -117.872937 8 Casuarina
cunninghamiana river she-oak Yes 19 1 19 0 0 0 0 35 25 Fair Fair top of tree is dead 34.150678 -117.87289 9 Platanus racemosa California sycamore No 0 1 0 0 0 0 0 0 0 Dead Dead 34.150686 -117.872848 10 Cedrus deodora deodar cedar No 15 1 15 0 0 0 0 45 20 Dead Dead 34.150612 -117.87275 11 Jacaranda mimosifolia jacaranda Yes 18 2 10 8 0 0 0 30 30 Fair Fair 34.150597 -117.87272 12 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 18 Poor Fair 34.150632 -117.872705 13 Quercus agrifolia coast live oak Yes 15 2 8 7 0 0 0 10 10 Fair Poor 34.150677 -117.87271 14 Washingtonia robusta Mexican fan palm Yes 11 1 11 0 0 0 0 75 15 Good Fair 34.150672 -117.872732 15 Washingtonia robusta Mexican fan palm No 8 1 8 0 0 0 0 10 8 Good Good 34.150716 -117.872648 16 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 10 Good Poor 34.15072 -117.872659 17 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 95 15 Good Fair 34.15072 -117.872661 18 Washingtonia robusta Mexican fan palm Yes 17 1 17 0 0 0 0 20 10 Good Good 34.150739 -117.87267 19 Casuarina
cunninghamiana river she-oak Yes 14 1 14 0 0 0 0 50 20 Fair Good 34.150788 -117.872658 20 Cedrus deodora deodar cedar Yes 20 1 20 0 0 0 0 50 30 Fair Fair 34.150746 -117.87279 21 Phoenix canariensis Canary Island date palm Yes 20 1 20 0 0 0 0 60 20 Good Good 34.150766 -117.872992 22 Cedrus deodora deodar cedar Yes 23 1 23 0 0 0 0 55 25 Fair Fair 34.150853 -117.872992 23 Cedrus deodora deodar cedar No 24 1 24 0 0 0 0 55 25 Dead Dead 34.150905 -117.873016 24 Phoenix canariensis Canary Island date palm Yes 18 1 18 0 0 0 0 45 18 Good Good 34.150911 -117.873094 25 Cedrus deodora deodar cedar Yes 17 1 17 0 0 0 0 40 20 Fair Fair 34.150973 -117.873058 26 Cedrus deodora deodar cedar No 18 1 18 0 0 0 0 45 15 Dead Dead 34.150876 -117.872862 27 Casuarina river she-oak Yes 10 1 10 0 0 0 0 30 15 Poor Poor mostly dead 34.150911 -117.872833 28 Casuarina
cunninghamiana river she-oak Yes 21 1 21 0 0 0 0 55 18 Fair Poor 34.150833 -117.872744 29 Pinus canariensis Canary Island pine Yes 24 1 24 0 0 0 0 55 20 Fair Fair top of tree is dead 34.150877 -117.872735 30 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 40 10 Fair Good 34.150892 -117.872617 31 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 45 12 Good Good 34.150938 -117.872606 32 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 25 10 Good Good 34.150959 -117.872609 33 Casuarina
cunninghamiana river she-oak Yes 15 1 15 0 0 0 0 35 20 Fair Fair top of tree is dead 34.150933 -117.87275 34 Grevillea robusta silk oak Yes 22 1 22 0 0 0 0 50 20 Good Fair 34.150985 -117.872734 35 Casuarina
cunninghamiana river she-oak Yes 15 1 15 0 0 0 0 35 15 Fair Fair top of tree is dead 34.150947 -117.872792 36 Casuarina
cunninghamiana river she-oak Yes 18 1 18 0 0 0 0 50 20 Good Fair 34.150948 -117.872857 37 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 30 10 Fair Good 34.15109 -117.872625 38 Casuarina
cunninghamiana river she-oak Yes 20 1 20 0 0 0 0 55 25 Good Fair 34.151083 -117.872707 39 Grevillea robusta silk oak Yes 25 1 25 0 0 0 0 55 25 Poor Poor 34.151115 -117.872748 40 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 50 15 Good Good 34.151104 -117.872832 41 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 50 15 Good Good 34.151081 -117.872853 42 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 45 15 Good Poor 34.151076 -117.872906 43 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 55 12 Good Poor 34.151114 -117.872879 44 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 60 12 Good Fair 34.151178 -117.872927 2020 Grand Estates Tree Information Matrix (ALL TREES)
Item #8. Page 782
Meeting Date: 1/24/2023 / Packet Page #: 847
45 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 60 12 Good Fair 34.151145 -117.872971 46 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 60 12 Good Fair 34.151209 -117.872978 47 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 60 12 Good Fair 34.151225 -117.872912 48 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 60 12 Good Fair 34.151255 -117.872967 49 Phoenix canariensis Canary Island date palm Yes 20 1 20 0 0 0 0 25 15 Good Good 34.151237 -117.87302 50 Phoenix canariensis Canary Island date palm Yes 21 1 21 0 0 0 0 30 20 Good Good 34.151175 -117.87302 51 Phoenix canariensis Canary Island date palm No 19 1 19 0 0 0 0 20 0 Dead Dead main stem is dead, stump
sprout at base 34.151089 -117.872996
52 Cedrus deodora deodar cedar Yes 23 1 23 0 0 0 0 50 30 Fair Fair 34.151141 -117.873076 53 Pinus canariensis Canary Island pine Yes 17 1 17 0 0 0 0 55 20 Fair Poor 34.151166 -117.872741 54 Pinus canariensis Canary Island pine Yes 11 1 11 0 0 0 0 30 15 Fair Fair 34.151243 -117.872795 55 Pinus canariensis Canary Island pine Yes 27 1 27 0 0 0 0 70 30 Fair Fair 34.15127 -117.872748 56 Pinus canariensis Canary Island pine Yes 21 1 21 0 0 0 0 70 30 Fair Fair 34.151273 -117.87282 57 Pinus canariensis Canary Island pine Yes 20 1 20 0 0 0 0 70 20 Fair Fair 34.151293 -117.872866 58 Pinus canariensis Canary Island pine Yes 17 1 17 0 0 0 0 60 15 Poor Fair 34.15133 -117.872845 59 Pinus canariensis Canary Island pine Yes 19 1 19 0 0 0 0 65 15 Fair Poor 34.151334 -117.872927 60 Pinus canariensis Canary Island pine Yes 22 1 22 0 0 0 0 70 20 Fair Fair 34.151296 -117.872945 61 Pinus canariensis Canary Island pine Yes 22 1 22 0 0 0 0 65 20 Good Fair 34.151295 -117.873071 62 Pinus canariensis Canary Island pine Yes 23 1 23 0 0 0 0 65 20 Fair Fair 34.15133 -117.873115 63 Pinus canariensis Canary Island pine Yes 22 1 22 0 0 0 0 65 20 Poor Fair 34.151392 -117.873112 64 Pinus canariensis Canary Island pine Yes 20 1 20 0 0 0 0 60 15 Fair Poor 34.151353 -117.87303 65 Pinus canariensis Canary Island pine Yes 17 1 17 0 0 0 0 55 10 Poor Poor 34.151381 -117.873028 66 Pinus canariensis Canary Island pine Yes 12 1 12 0 0 0 0 40 10 Fair Poor 34.151408 -117.87308 67 Pinus canariensis Canary Island pine Yes 20 1 20 0 0 0 0 60 15 Fair Fair 34.151403 -117.872953 68 Pinus canariensis Canary Island pine Yes 21 1 21 0 0 0 0 60 15 Fair Fair 34.15139 -117.872894 69 Pinus canariensis Canary Island pine Yes 22 1 22 0 0 0 0 60 15 Fair Fair 34.151435 -117.872937 70 Pinus canariensis Canary Island pine Yes 23 1 23 0 0 0 0 60 15 Fair Fair 34.15143 -117.872984 71 Pinus canariensis Canary Island pine Yes 19 1 19 0 0 0 0 75 15 Fair Fair 34.151476 -117.873008 72 Pinus canariensis Canary Island pine Yes 20 1 20 0 0 0 0 75 15 Fair Fair 34.151505 -117.872961 73 Pinus canariensis Canary Island pine Yes 22 1 22 0 0 0 0 75 20 Fair Poor 34.151498 -117.87286 74 Pinus canariensis Canary Island pine Yes 22 1 22 0 0 0 0 70 15 Fair Poor 34.151557 -117.872898 75 Eucalyptus robusta swamp mahogany No 20 1 20 0 0 0 0 20 10 Dead Dead 34.151564 -117.872847 76 Eucalyptus robusta swamp mahogany Yes 15 1 15 0 0 0 0 15 20 Good Poor 34.15157 -117.872935 77 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 30 12 Good Good 34.151731 -117.873021 78 Olea europaea fruitless olive Yes 12 1 12 0 0 0 0 20 20 Good Fair 34.151655 -117.873041 79 Quercus agrifolia coast live oak Yes 26 4 9 9 4 4 0 20 20 Good Fair 34.151621 -117.872866 80 Heteromeles toyon Yes 21 5 7 5 5 4 0 15 15 Poor Fair 34.151508 -117.873067 81 Quercus agrifolia coast live oak No 8 1 8 0 0 0 0 0 0 Dead Dead laying on ground 34.151519 -117.8731 82 Grevillea robusta silk oak Yes 24 1 24 0 0 0 0 65 30 Fair Fair 34.15155 -117.873121 83 Olea europaea fruitless olive Yes 26 3 10 10 6 0 0 30 30 Good Poor 34.151585 -117.873099 84 Grevillea robusta silk oak Yes 18 1 18 0 0 0 0 55 20 Fair Fair 34.151607 -117.87315 85 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 8 0 Dead Dead 34.15163 -117.873137 86 Grevillea robusta silk oak Yes 20 1 20 0 0 0 0 55 15 Good Good 34.15167 -117.873145 87 Grevillea robusta silk oak Yes 19 1 19 0 0 0 0 50 15 Fair Fair 34.151595 -117.873218 88 Grevillea robusta silk oak Yes 16 1 16 0 0 0 0 45 15 Fair Fair 34.151534 -117.87318 89 Cedrus deodora deodar cedar No 13 1 13 0 0 0 0 35 15 Dead Dead 34.151339 -117.873174 90 Cedrus deodora deodar cedar Yes 26 1 26 0 0 0 0 55 30 Fair Fair 34.151316 -117.873162 91 Grevillea robusta silk oak Yes 11 1 11 0 0 0 0 40 15 Good Fair 34.151366 -117.873156 Item #8. Page 783
Meeting Date: 1/24/2023 / Packet Page #: 848
92 Grevillea robusta silk oak No 9 1 9 0 0 0 0 30 10 Fair Fair 34.151379 -117.873171 93 Cedrus deodora deodar cedar No 16 1 16 0 0 0 0 45 20 Dead Dead fell into adjacent tree,
presents hazard, should be
removed 34.151378 -117.87322
94 Casuarina
cunninghamiana river she-oak Yes 14 1 14 0 0 0 0 35 15 Fair Fair 34.151415 -117.873195 95 Casuarina river she-oak No 13 1 13 0 0 0 0 35 10 Dead Dead 34.151439 -117.873151 96 Olea europaea fruitless olive Yes 20 2 10 10 0 0 0 30 30 Good Fair 34.151449 -117.87328 97 Cedrus deodora deodar cedar No 26 1 26 0 0 0 0 55 20 Dead Dead 34.151563 -117.873318 98 Cedrus deodora deodar cedar No 16 1 16 0 0 0 0 40 20 Dead Dead 34.151628 -117.873393 99 Quercus agrifolia coast live oak No 0 1 0 0 0 0 0 0 0 Dead Dead laying on ground 34.151722 -117.873455 100 Cedrus deodora deodar cedar No 21 1 21 0 0 0 0 55 20 Dead Dead 34.151699 -117.873489 102 Cedrus deodora deodar cedar Yes 31 1 31 0 0 0 0 65 30 Fair Good 34.151757 -117.873573 103 Arucaria bidwillii bunya-bunya Yes 20 1 20 0 0 0 0 55 20 Fair Fair 34.151827 -117.873463 104 Arucaria bidwillii bunya-bunya Yes 16 1 16 0 0 0 0 55 15 Fair Fair 34.151884 -117.873501 105 Cedrus deodora deodar cedar No 30 1 30 0 0 0 0 65 30 Dead Dead 34.151977 -117.873743 107 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 30 35 Good Fair 34.151819 -117.87401 108 Quercus agrifolia coast live oak Yes 36 1 36 0 0 0 0 35 40 Good Poor 34.151867 -117.874158 109 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 35 30 Good Fair 34.151924 -117.874379 110 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 15 Good Fair 34.15193 -117.874396 111 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 25 20 Good Fair 34.152112 -117.874571 112 Quercus agrifolia coast live oak Yes 35 1 35 0 0 0 0 45 40 Good Fair 34.152039 -117.874605 113 Cedrus deodora deodar cedar Yes 11 1 11 0 0 0 0 45 15 Fair Fair 34.152157 -117.874717 114 Pseudotsaya menziesii Douglas-fir Yes 13 1 13 0 0 0 0 40 10 Dead Dead 34.152179 -117.874815 115 Pseudotsaya menziesii Douglas-fir Yes 12 1 12 0 0 0 0 40 8 Poor Poor 34.1522 -117.874874 116 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 25 Good Fair 34.15222 -117.87506 117 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 20 Good Fair 34.15225 -117.875191 118 Prunus domestica fruiting plum No 8 1 8 0 0 0 0 20 15 Good Fair 34.152294 -117.87526 119 Phoenix canariensis Canary Island date palm Yes 23 1 23 0 0 0 0 35 20 Good 34.152379 -117.874487 120 Phoenix canariensis Canary Island date palm Yes 17 1 17 0 0 0 0 30 15 Good Fair 34.152361 -117.874464 121 Phoenix canariensis Canary Island date palm Yes 20 1 20 0 0 0 0 40 15 Good Good 34.152427 -117.874258 122 Phoenix canariensis Canary Island date palm Yes 20 1 20 0 0 0 0 40 15 Fair Good 34.152361 -117.87427 123 Phoenix canariensis Canary Island date palm Yes 19 1 19 0 0 0 0 40 15 Fair Good 34.152323 -117.874265 124 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152242 -117.875529 125 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152308 -117.875561 126 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.15228 -117.875594 127 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152284 -117.875651 128 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152347 -117.875561 129 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.15233 -117.875641 130 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.15235 -117.87568 131 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152386 -117.875671 132 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152387 -117.875708 133 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152429 -117.875676 134 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152435 -117.875744 135 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152484 -117.875745 136 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152486 -117.875724 137 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152483 -117.875676 138 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152513 -117.8756 139 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 55 15 Fair Fair shares tag with #172 34.152574 -117.875609 Item #8. Page 784
Meeting Date: 1/24/2023 / Packet Page #: 849
140 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152521 -117.875673 141 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152555 -117.875744 142 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152539 -117.875775 143 Washingtonia robusta Mexican fan palm Yes 17 1 17 0 0 0 0 80 15 Good Fair 34.152594 -117.875837 144 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152624 -117.875768 145 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152657 -117.875771 146 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152668 -117.875861 147 Washingtonia robusta Mexican fan palm Yes 18 1 18 0 0 0 0 80 15 Good Fair 34.152681 -117.875998 148 Washingtonia robusta Mexican fan palm Yes 17 1 17 0 0 0 0 80 15 Good Fair 34.152678 -117.875969 149 Quercus agrifolia coast live oak Yes 40 1 40 0 0 0 0 45 50 Good Good 34.15229 -117.875558 150 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 20 Good Fair 34.152403 -117.875662 151 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 45 35 Fair Good 34.152435 -117.875635 152 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 25 20 Fair Fair 34.152446 -117.875581 153 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Fair 34.152467 -117.875682 154 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 25 20 Fair Fair 34.152484 -117.875701 155 Juglans californica Southern California No 6 1 6 0 0 0 0 0 0 Dead Dead laying on ground 34.152484 -117.875729 156 Schinus terebinthifolia Brazilian pepper No 6 1 6 0 0 0 0 25 20 Fair Fair 34.152522 -117.875725 157 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 50 35 Fair Fair 34.152548 -117.875712 158 Schinus terebinthifolia Brazilian pepper No 28 2 14 14 0 0 0 15 15 Dead Dead 34.152584 -117.875738 159 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 20 25 Fair Fair 34.152645 -117.875756 160 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Fair 34.152724 -117.875971 161 Quercus agrifolia coast live oak Yes 26 2 13 13 0 0 0 30 30 Fair Fair 34.152693 -117.875994 162 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 60 15 Fair Fair 34.152747 -117.875981 163 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 30 Fair Fair 34.152743 -117.875962 164 Heteromeles toyon No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152731 -117.875884 165 Heteromeles toyon No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152709 -117.875877 166 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 40 35 Fair Fair 34.152706 -117.875804 167 Quercus agrifolia coast live oak No 0 1 0 0 0 0 0 0 0 Dead Dead laying on ground 34.1527 -117.87569 168 Washingtonia robusta Mexican fan palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152664 -117.875656 169 Quercus agrifolia coast live oak Yes 29 2 15 14 0 0 0 30 30 Fair Poor 34.152625 -117.87564 170 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 30 Fair Fair 34.152619 -117.875592 171 Olea europaea fruitless olive Yes 20 2 10 10 0 0 0 30 25 Good Poor 34.152596 -117.87561 172 0 Shares tag with #139
173 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 45 30 Fair Fair 34.152496 -117.875526 174 Pinus pinea Italian stone pine Yes 50 1 50 0 0 0 0 40 40 Fair Poor 34.152215 -117.876008 175 Quercus agrifolia coast live oak Yes 20 2 11 9 0 0 0 20 20 Good Fair 34.152305 -117.876006 176 Juglans californica
Southern California
black walnut No 0 1 0 0 0 0 0 0 0 Dead Dead
main stem is dead, stump
sprout at base 34.152445 -117.875996
177 Juglans californica
Southern California black
walnut No 4 5 4 0 0 0 0 10 10 Fair Poor Stems of 3,3,2,1 34.152476 -117.876013 178 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152849 -117.872777 179 Quercus agrifolia coast live oak Yes 35 1 35 0 0 0 0 35 35 Fair Fair laying on ground 34.152909 -117.872791 180 Quercus agrifolia coast live oak Yes 30 1 30 0 0 0 0 40 25 Poor Poor 34.152865 -117.872593 181 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 10 0 Dead Dead 34.152876 -117.872569 182 Quercus agrifolia coast live oak Yes 10 2 6 4 0 0 0 18 10 Fair Poor 34.152847 -117.872536 183 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Fair Poor 34.152818 -117.872569 184 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Poor 34.152793 -117.872633 185 Quercus agrifolia coast live oak Yes 26 1 26 0 0 0 0 50 35 Fair Fair 34.152794 -117.872681 186 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 45 30 Fair Fair 34.152731 -117.872793 Item #8. Page 785
Meeting Date: 1/24/2023 / Packet Page #: 850
187 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 50 20 Fair Fair 34.152754 -117.87272 188 Quercus agrifolia coast live oak Yes 32 1 32 0 0 0 0 55 35 Fair Fair 34.152749 -117.872723 189 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 40 25 Fair Fair 34.152743 -117.872642 190 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 10 Fair Fair 34.152723 -117.872656 191 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Good Fair 34.15273 -117.872578 192 Quercus agrifolia coast live oak Yes 30 1 30 0 0 0 0 45 35 Fair Fair 34.152757 -117.872544 193 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 50 20 Fair Fair 34.152696 -117.872583 194 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 40 25 Fair Fair 34.152692 -117.872674 195 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 40 20 Fair Fair 34.152644 -117.87257 196 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 35 25 Fair Fair 34.152644 -117.872604 197 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 7 0 Dead Dead 34.152642 -117.872695 198 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 35 20 Fair Fair 34.152631 -117.872689 199 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Fair Fair 34.152606 -117.872674 200 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 45 20 Good Fair 34.152587 -117.872589 201 Quercus agrifolia coast live oak No 5 1 5 0 0 0 0 0 0 Dead Dead laying on ground 34.152544 -117.872688 202 Quercus agrifolia coast live oak No 5 1 5 0 0 0 0 0 0 Dead Dead laying on ground 34.15258 -117.872698 203 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 25 Fair Fair 34.152612 -117.872801 204 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 35 30 Fair Fair 34.152513 -117.872686 205 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 40 40 Fair Fair 34.152471 -117.872664 206 Quercus agrifolia coast live oak No 20 1 20 0 0 0 0 15 0 Dead Dead no tag 34.152512 -117.87273 207 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 25 Fair Poor 34.152497 -117.872683 208 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152486 -117.87269 209 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 10 6 Fair Poor 34.152499 -117.872745 210 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 15 10 Fair Fair 34.152497 -117.872777 211 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Fair Fair 34.152496 -117.872794 212 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 10 Fair Fair 34.152484 -117.872785 213 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 20 Good Fair 34.152463 -117.872777 214 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 15 10 Good Poor 34.152449 -117.872783 215 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 15 Good Fair 34.152475 -117.872815 216 Quercus agrifolia coast live oak No 8 1 8 0 0 0 0 15 0 Dead Dead 34.152491 -117.872866 217 Quercus agrifolia coast live oak Yes 28 2 16 12 0 0 0 20 15 Good Fair 34.152459 -117.872865 218 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.152392 -117.872701 219 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 8 Fair Poor 34.152384 -117.872711 220 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Fair 34.152332 -117.872756 221 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 13 Fair Fair 34.152318 -117.872761 222 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152363 -117.87284 223 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152312 -117.872885 224 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.15229 -117.872851 225 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152248 -117.87289 226 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152246 -117.872889 227 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152245 -117.872891 228 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152246 -117.872891 229 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152224 -117.872881 230 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.15223 -117.872849 231 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.152252 -117.872835 232 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 20 20 Fair Poor 34.152239 -117.872832 233 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 0 0 Dead Dead laying on ground 34.15224 -117.872861 234 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 10 0 Dead Dead 34.152263 -117.872822 235 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Fair Fair 34.152362 -117.872642 Item #8. Page 786
Meeting Date: 1/24/2023 / Packet Page #: 851
236 Quercus agrifolia coast live oak 0 unable to locate 237 Quercus agrifolia coast live oak No 15 1 15 0 0 0 0 0 0 Dead Dead laying on ground 34.152248 -117.872579 238 Quercus agrifolia coast live oak Yes 38 3 12 13 13 0 0 30 30 Good Fair 34.152219 -117.8727 239 Quercus agrifolia coast live oak No 12 1 12 0 0 0 0 10 0 Dead Dead 34.152179 -117.872697 240 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 20 Fair Fair 34.152154 -117.87285 241 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 20 15 Fair Fair 34.152159 -117.872822 242 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Poor 34.152165 -117.872817 243 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 20 15 Fair Fair 34.152166 -117.872795 244 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 12 Fair Fair 34.152151 -117.872802 245 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 12 Fair Fair 34.152145 -117.872799 246 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 6 10 Fair Poor 34.152122 -117.872841 247 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 18 10 Fair Fair 34.152042 -117.872651 248 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 15 10 Fair Fair 34.152085 -117.872799 249 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 20 15 Fair Fair 34.152114 -117.872655 250 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 5 0 Dead Dead 34.152239 -117.87262 251 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 20 20 Fair Fair 34.152076 -117.872732 252 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 15 6 Fair Poor 34.15209 -117.872778 253 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 20 10 Poor Poor 34.152052 -117.872751 254 Olea europaea fruitless olive No 0 4 0 0 0 0 0 10 5 Poor Poor stump sprout, stems of
3,3,3,3 34.152743 -117.872819
255 Olea europaea fruitless olive Yes 22 2 22 0 0 0 0 35 25 Fair Fair 34.152769 -117.872841 256 Olea europaea fruitless olive Yes 18 1 18 0 0 0 0 30 20 Fair Poor 34.152581 -117.872744 257 Olea europaea fruitless olive Yes 22 3 22 0 0 0 0 20 15 Fair Poor 34.152295 -117.872785 258 Olea europaea fruitless olive Yes 25 3 25 0 0 0 0 30 25 Fair Poor 34.152312 -117.872683 259 Olea europaea fruitless olive Yes 14 3 14 0 0 0 0 15 15 Fair Poor 34.152327 -117.872715 260 Olea europaea fruitless olive Yes 13 1 13 0 0 0 0 15 20 Poor Poor 34.152286 -117.872692 261 Olea europaea fruitless olive Yes 16 2 16 0 0 0 0 15 15 Fair Poor 34.152322 -117.873081 262 Olea europaea fruitless olive Yes 24 3 24 0 0 0 0 25 30 Fair Poor 34.152244 -117.873053 263 Olea europaea fruitless olive Yes 50 5 10 10 10 10 10 25 30 Fair Poor 34.152031 -117.872723 264 Olea europaea fruitless olive Yes 18 4 18 0 0 0 0 25 30 Good Poor 34.151664 -117.872945 265 Olea europaea fruitless olive Yes 18 1 18 0 0 0 0 30 20 Good Poor 34.151654 -117.87316 266 Ceratonia siliqua carob Yes 28 1 28 0 0 0 0 30 50 Fair Fair 34.15157 -117.873313 267 0
Not on arborist map, no
inventory information
268 0
Not on arborist map, no
inventory information
269 0
Not on arborist map, no
inventory information
270 Pinus canariensis Canary Island pine Yes 18 1 18 0 0 0 0 65 15 Poor Poor 34.152701 -117.875494 271 Quercus agrifolia coast live oak No 17 1 17 0 0 0 0 10 2 Dead Dead 34.15274 -117.875433 272 Pinus canariensis Canary Island pine Yes 33 1 33 0 0 0 0 70 35 Fair Poor 34.152695 -117.875429 273 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 30 Fair Fair 34.152693 -117.875472 274 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 15 Fair Fair 34.152713 -117.875384 275 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 15 Fair Poor 34.152691 -117.875335 276 0 unable to locate
277 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 45 30 Good Fair 34.152598 -117.875291 278 Arbutus unedo strawberry madrone No 7 1 7 0 0 0 0 12 10 Good Fair 34.152563 -117.875281 279 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 50 30 Fair Fair 34.152538 -117.875163 280 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 20 Good Fair 34.152569 -117.875079 Item #8. Page 787
Meeting Date: 1/24/2023 / Packet Page #: 852
281 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 50 30 Poor Fair 34.152535 -117.875093 282 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 25 Fair Fair 34.152551 -117.875026 283 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Poor 34.152544 -117.874848 284 0 unable to locate
285 Quercus agrifolia coast live oak Yes 20 2 20 0 0 0 0 35 30 Fair Fair 34.152559 -117.874573 286 0 unable to locate
287 0 unable to locate
288 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 75 15 Fair Fair 34.152826 -117.875749 289 Washingtonia robusta Mexican fan palm Yes 18 1 18 0 0 0 0 75 15 Fair Fair 34.152747 -117.875938 290 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 20 20 Fair Fair 34.152748 -117.875939 291 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 75 15 Fair Fair 34.152808 -117.875918 292 Olea europaea fruitless olive Yes 24 2 24 0 0 0 0 20 15 Poor Poor 34.152835 -117.875938 293 Washingtonia robusta Mexican fan palm Yes 17 1 17 0 0 0 0 75 15 Fair Fair 34.15287 -117.875938 294 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 30 30 Poor Poor 34.152909 -117.875945 295 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 10 10 Fair Poor 34.15289 -117.875995 296 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 20 20 Fair Fair 34.152847 -117.876094 297 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Fair Fair 34.15286 -117.876102 298 Washingtonia robusta Mexican fan palm Yes 15 1 15 0 0 0 0 75 15 Fair Fair 34.152765 -117.876073 300 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 35 40 Fair Fair 34.152833 -117.876238 303 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 6 4 Good Poor stump sprout 34.152896 -117.876214 304 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 20 Poor Poor 34.152988 -117.876181 305 Quercus agrifolia coast live oak No 25 1 25 0 0 0 0 0 0 Dead Dead 34.153016 -117.876141 306 Quercus agrifolia coast live oak No 29 1 29 0 0 0 0 0 0 Dead Dead 34.1531 -117.87619 307 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 15 10 Fair Fair 34.153127 -117.876209 308 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.153161 -117.87621 309 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 30 Fair Fair 34.153193 -117.876233 310 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 15 Fair Fair 34.153132 -117.87616 311 Quercus agrifolia coast live oak no 12 1 12 0 0 0 0 10 0 Dead Dead 34.153134 -117.876158 312 Quercus agrifolia coast live oak 13 1 13 0 0 0 0 10 10 Poor Poor 34.153133 -117.876159 313 0 unable to locate
314 Corymbia maculata spotted gum Yes 38 1 38 0 0 0 0 90 45 Poor Poor 34.153041 -117.875942 315 Corymbia maculata spotted gum No 13 1 13 0 0 0 0 40 10 Dead Dead 34.152919 -117.87588 316 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 20 Poor Poor 34.152913 -117.875847 317 Corymbia maculata spotted gum No 40 1 40 0 0 0 0 50 20 Dead Dead 34.152826 -117.875777 318 Washingtonia robusta Mexican fan palm Yes 10 1 10 0 0 0 0 75 15 Fair Fair 34.152814 -117.875748 319 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 30 Fair Fair 34.153339 -117.876312 320 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 20 Fair Fair 34.15333 -117.876311 321 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 35 Fair Fair 34.153346 -117.876303 322 Quercus agrifolia coast live oak Yes 58 1 58 0 0 0 0 40 40 Fair Fair 34.153447 -117.876347 323 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 15 Fair Fair 34.153473 -117.876336 324 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 20 Fair Fair 34.153447 -117.876292 325 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Fair Fair 34.153514 -117.876323 326 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Fair Fair 34.153513 -117.876323 327 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 20 Fair Fair 34.153639 -117.876215 328 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 20 Fair Fair 34.153665 -117.876267 329 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 35 30 Fair Fair 34.153496 -117.876255 330 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 18 Fair Fair 34.15349 -117.876181 331 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 40 20 Fair Fair 34.15348 -117.876208 Item #8. Page 788
Meeting Date: 1/24/2023 / Packet Page #: 853
332 Juglans californica
Southern California black
walnut Yes 10 2 10 0 0 0 0 40 30 Fair Fair 34.153492 -117.876198 333 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 30 Fair Poor 34.153478 -117.876282 334 Juglans californica
Southern California black
walnut Yes 21 2 21 0 0 0 0 30 30 Fair Poor 34.153435 -117.876186 335 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 40 20 Fair Fair 34.153433 -117.8762 336 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 20 Fair Fair 34.153447 -117.876166 337 Corymbia maculata spotted gum Yes 39 2 39 0 0 0 0 50 40 Fair Fair 34.153336 -117.876254 338 Corymbia maculata spotted gum Yes 44 1 44 0 0 0 0 55 50 Fair Fair 34.153279 -117.876211 339 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 15 Fair Poor 34.153264 -117.876115 340 Juglans californica
Southern California black
walnut Yes 19 3 19 0 0 0 0 25 20 Fair Fair 34.15325 -117.87598 341 Quercus agrifolia coast live oak Yes 11 2 11 0 0 0 0 20 15 Fair Fair 34.153246 -117.875961 342 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Fair 34.153193 -117.875921 343 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Good Poor 34.153172 -117.875897 344 Quercus agrifolia coast live oak Yes 21 2 21 0 0 0 0 30 23 Good Fair 34.153155 -117.875826 345 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 30 15 Poor Poor 34.153128 -117.875914 346 Eucalyptus robusta swamp mahogany No 27 1 27 0 0 0 0 55 40 Dead Dead 34.153093 -117.875917 347 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Fair Fair 34.153029 -117.875732 348 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 30 Fair Fair 34.153084 -117.875778 349 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 15 15 Fair Poor 34.153136 -117.875708 350 Quercus agrifolia coast live oak No 19 2 19 0 0 0 0 25 15 Dead Dead 34.15312 -117.875718 351 Juglans californica
Southern California black
walnut Yes 8 1 8 0 0 0 0 30 15 Fair Poor 34.153059 -117.875488 352 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 25 15 Fair Fair 34.153056 -117.875681 353 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Fair 34.153023 -117.875672 354 Eucalyptus robusta swamp mahogany No 41 1 41 0 0 0 0 35 25 Dead Dead 34.152967 -117.875613 355 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Poor 34.153005 -117.875521 356 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 20 Fair Fair 34.152896 -117.875492 357 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 20 Fair Fair 34.152856 -117.875505 358 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 12 9 Good Poor 34.152829 -117.87547 359 Corymbia maculata spotted gum Yes 31 1 31 0 0 0 0 50 40 Poor Poor 34.152862 -117.875482 360 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Fair Fair 34.152809 -117.875488 361 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Fair Fair 34.152868 -117.875458 362 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 40 20 Fair Fair 34.152858 -117.875424 363 Juglans californica Southern California Yes 10 2 5 5 0 0 0 20 10 Poor Poor stem of 3 34.152821 -117.875322 364 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 10 20 Poor Poor broke in half 34.152818 -117.875302 365 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Fair Fair 34.152811 -117.875356 366 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Fair Fair 34.152808 -117.875364 367 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Fair Fair 34.152801 -117.87537 368 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 15 9 Good Poor 34.152776 -117.875421 369 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 6 4 Poor Poor stump sprout 34.152767 -117.875366 370 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 25 20 Fair Fair 34.152759 -117.875356 371 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 20 Fair Fair 34.152754 -117.875273 372 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Fair 34.152751 -117.875264 373 Juglans californica Southern California Yes 11 1 11 0 0 0 0 15 7 Dead Dead 34.152731 -117.875313 374 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 20 Good Fair 34.15274 -117.875208 375 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 40 30 Good Fair 34.152721 -117.875189 376 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 20 Good Fair 34.152732 -117.875168 377 Juglans californica
Southern California black
walnut Yes 16 3 6 5 5 0 0 15 15 Fair Poor 34.152737 -117.875123 378 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 40 25 Good Fair 34.152668 -117.875156 379 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Good Fair 34.152682 -117.875226 Item #8. Page 789
Meeting Date: 1/24/2023 / Packet Page #: 854
380 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Good Fair 34.152685 -117.87526 381 Juglans californica
Southern California black
walnut Yes 24 4 8 8 4 4 0 15 15 Fair Fair 34.153116 -117.875335 382 Juglans californica
Southern California black
walnut Yes 20 4 6 6 4 4 0 15 15 Fair Fair 34.153095 -117.875392 383 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Good Fair 34.152646 -117.875254 384 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 14 Good Fair 34.15261 -117.875248 385 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 40 20 Good Fair 34.152599 -117.875249 386 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Good Fair 34.152643 -117.875217 387 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Good Fair 34.152615 -117.875171 388 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 15 Fair Fair 34.15257 -117.875169 389 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 40 25 Good Fair 34.152589 -117.875136 390 Quercus agrifolia coast live oak No 0 1 0 0 0 0 0 6 4 Poor Poor broke below dbh 34.152563 -117.875155 391 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 10 Good Fair 34.152566 -117.875092 392 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Good Fair 34.152643 -117.875105 393 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 20 Fair Fair 34.152688 -117.875039 394 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 12 10 Good Poor 34.152689 -117.875082 395 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 40 20 Fair Fair 34.152622 -117.87499 396 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Fair 34.152612 -117.874987 397 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 45 30 Good Fair 34.152598 -117.875008 398 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 15 Fair Poor 34.15259 -117.875034 399 Quercus agrifolia coast live oak Yes 17 2 9 8 0 0 0 35 20 Fair Poor 34.15257 -117.874984 400 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Fair Poor 34.152591 -117.874926 401 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 20 Fair Fair 34.152574 -117.874935 402 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 40 30 Good Fair 34.152568 -117.874952 403 Ceratonia siliqua carob Yes 48 4 16 16 10 6 0 30 20 Good Fair 34.152621 -117.874893 404 No 14 1 14 0 0 0 0 20 0 Dead Dead 34.152594 -117.874834 405 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 15 Fair Poor 34.152595 -117.874874 406 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 15 Fair Fair 34.152596 -117.874878 407 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 40 20 Good Fair 34.152548 -117.874745 408 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 45 20 Good Fair 34.152563 -117.874757 409 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Good 34.15258 -117.87477 410 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Poor Poor 34.152615 -117.874772 411 Quercus agrifolia coast live oak Yes 20 2 20 0 0 0 0 40 15 Fair Poor 34.152655 -117.874789 412 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 45 15 Fair Poor 34.152672 -117.874794 413 0 unable to locate
414 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 15 Fair Poor 34.152689 -117.87479 415 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 40 15 Fair Poor 34.152699 -117.874759 416 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 35 15 Fair Poor 34.152684 -117.874733 417 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 40 15 Fair Poor 34.152724 -117.874791 418 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Poor 34.152724 -117.874787 419 Quercus agrifolia coast live oak Yes 21 2 21 0 0 0 0 40 20 Fair Poor 34.152746 -117.874776 420 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 40 15 Fair Poor 34.152798 -117.874783 421 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 25 Fair Fair 34.152794 -117.874809 422 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 35 30 Fair Fair 34.152839 -117.874754 423 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 30 Fair Fair 34.152844 -117.874754 424 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 45 30 Good Fair 34.152852 -117.874738 425 Quercus agrifolia coast live oak Yes 29 3 29 0 0 0 0 45 30 Fair Fair 34.152821 -117.87469 426 Quercus agrifolia coast live oak Yes 28 4 28 0 0 0 0 40 40 Fair Fair 34.152805 -117.874706 Item #8. Page 790
Meeting Date: 1/24/2023 / Packet Page #: 855
427 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.152808 -117.874714 428 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 40 15 Fair Poor 34.152741 -117.874749 429 Quercus agrifolia coast live oak Yes 18 2 18 0 0 0 0 35 15 Fair Poor 34.152717 -117.874755 430 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 10 Fair Poor 34.152729 -117.874775 431 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 15 Fair Poor 34.152718 -117.874705 432 Quercus agrifolia coast live oak Yes 24 3 24 0 0 0 0 30 15 Fair Poor 34.152701 -117.874656 433 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.152632 -117.874666 434 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 15 Fair Poor 34.152627 -117.874674 435 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 25 Fair Fair 34.152632 -117.874701 436 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 45 30 Good Fair 34.152602 -117.874694 437 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 20 Good Fair 34.152562 -117.874715 438 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 70 15 Fair Fair 34.152649 -117.874586 439 Platanus racemosa California sycamore No 15 1 15 0 0 0 0 15 10 Dead Dead main stem is dead, stump
sprout at base 34.152681 -117.874566
440 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 65 15 Fair Fair 34.15271 -117.874589 441 Casuarina river she-oak No 24 1 24 0 0 0 0 40 20 Dead Dead 34.152737 -117.874567 442 Washingtonia robusta Mexican fan palm Yes 12 1 12 0 0 0 0 55 15 Fair Fair 34.152777 -117.874596 443 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 55 15 Fair Fair 34.152807 -117.874638 444 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 65 15 Fair Fair 34.152913 -117.874621 445 Washingtonia robusta Mexican fan palm Yes 10 1 10 0 0 0 0 55 15 Fair Fair 34.152939 -117.874619 446 Platanus racemosa California sycamore Yes 10 1 10 0 0 0 0 18 15 Fair Poor stump sprout 34.153132 -117.874819 447 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Poor stump sprout 34.153127 -117.874747 448 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 18 Good Poor stump sprout 34.153096 -117.874723 449 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 18 Good Poor stump sprout 34.153106 -117.874707 450 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 35 20 Fair Poor stump sprout 34.153248 -117.874787 451 Quercus agrifolia coast live oak Yes 47 1 47 0 0 0 0 40 40 Fair Fair stump sprout 34.153279 -117.874872 452 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 20 30 Poor Poor stump sprout 34.153282 -117.874904 453 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 18 Poor Poor stump sprout 34.15332 -117.874874 454 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 20 Fair Poor stump sprout 34.15331 -117.874828 455 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 40 15 Fair Poor stump sprout 34.153338 -117.874805 456 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 40 45 Fair Poor stump sprout 34.153371 -117.87476 457 Platanus racemosa California sycamore No 8 1 8 0 0 0 0 0 0 Dead Dead 34.153355 -117.874758 458 Washingtonia robusta Mexican fan palm Yes 16 1 16 0 0 0 0 60 15 Good Fair 34.153369 -117.874514 459 Juglans californica
Southern California black
walnut Yes 42 3 42 0 0 0 0 25 30 Fair Poor 34.153446 -117.874664 460 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 45 30 Fair Fair 34.153465 -117.874497 461 Phoenix canariensis Canary Island date palm Yes 28 1 28 0 0 0 0 30 20 Fair Fair 34.153342 -117.874494 462 Phoenix canariensis Canary Island date palm Yes 26 1 26 0 0 0 0 10 15 Good Fair 34.153352 -117.874514 463 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 14 Good Good 34.153556 -117.874486 464 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 30 30 Poor Poor 34.153271 -117.874447 465 Quercus agrifolia coast live oak Yes 22 2 14 8 0 0 0 40 20 Fair Fair 34.153156 -117.874447 466 Quercus agrifolia coast live oak Yes 19 2 11 8 0 0 0 30 20 Fair Fair 34.153162 -117.874455 467 Quercus agrifolia coast live oak Yes 26 2 13 13 0 0 0 40 20 Fair Fair 34.153106 -117.87443 468 Quercus agrifolia coast live oak Yes 32 1 32 0 0 0 0 40 30 Fair Poor 34.153085 -117.874403 469 0 unable to locate
470 Quercus agrifolia coast live oak Yes 32 1 32 0 0 0 0 45 35 Fair Fair 34.152917 -117.874505 471 Juglans californica
Southern California black
walnut Yes 18 1 18 0 0 0 0 20 30 Fair Poor 34.153134 -117.874458 472 0 unable to locate
473 0 unable to locate
Item #8. Page 791
Meeting Date: 1/24/2023 / Packet Page #: 856
474 0 unable to locate
475 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 50 20 Fair Fair 34.152891 -117.874513 476 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 20 Fair Fair 34.152904 -117.874519 477 0 unable to locate
478 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 45 25 Fair Fair 34.152849 -117.874368 479 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 25 20 Good Good 34.152849 -117.874377 480 Quercus agrifolia coast live oak Yes 43 7 7 9 9 9 9 30 40 Fair Poor additonal stems 7,7 34.152807 -117.87433 481 0 unable to locate
482 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 14 Good Fair 34.152765 -117.874388 483 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 18 Good Fair 34.152753 -117.874416 484 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 14 Good Poor 34.152724 -117.874349 485 Quercus agrifolia coast live oak Yes 41 4 41 0 0 0 0 40 35 Fair Fair 34.152793 -117.874448 486 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 20 Good Fair 34.152814 -117.874405 487 Quercus agrifolia coast live oak Yes 17 3 17 0 0 0 0 50 30 Good Fair 34.152835 -117.874547 488 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 50 25 Fair Fair 34.152825 -117.874557 489 Quercus agrifolia coast live oak Yes 27 2 27 0 0 0 0 35 30 Fair Poor 34.152806 -117.874549 490 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 8 Good Poor 34.152646 -117.874352 491 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Good Fair 34.152609 -117.874309 492 Olea europaea fruitless olive Yes 16 4 16 0 0 0 0 20 20 Good Poor 34.152587 -117.874374 493 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 0 0 Dead Dead 34.152633 -117.874268 494 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 25 Fair Fair 34.15259 -117.874462 495 Sambucus canadensis American elderberry Yes 11 2 11 0 0 0 0 15 20 Fair Fair 34.152537 -117.874398 496 Pinus canariensis Canary Island pine No 24 1 24 0 0 0 0 75 15 Dead Dead 34.152546 -117.874211 497 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 12 10 Fair Poor 34.152605 -117.874256 498 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 35 15 Fair Poor 34.152621 -117.874208 499 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 12 Fair Poor 34.152604 -117.874221 500 Olea europaea fruitless olive Yes 23 2 23 0 0 0 0 20 25 Good Poor 34.152495 -117.874281 501 Olea europaea fruitless olive Yes 11 1 11 0 0 0 0 40 20 Fair Fair 34.152677 -117.874138 502 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 25 20 Fair Fair 34.152746 -117.87416 503 Olea europaea fruitless olive Yes 30 5 30 0 0 0 0 35 30 Good Poor 34.152759 -117.874242 504 Juglans californica
Southern California black
walnut Yes 12 2 12 0 0 0 0 15 15 Fair Fair 34.152768 -117.874175 505 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 35 20 Fair Fair 34.152695 -117.874086 506 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 20 Fair Fair 34.152627 -117.874055 507 Olea europaea fruitless olive Yes 12 2 12 0 0 0 0 20 20 Fair Poor 34.152597 -117.874081 508 Pinus canariensis Canary Island pine Yes 28 1 28 0 0 0 0 70 25 Fair Poor 34.152535 -117.87406 509 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 16 8 Poor Poor stump sprout 34.152564 -117.874061 510 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 20 Fair Fair 34.152643 -117.874016 511 Olea europaea fruitless olive No 20 2 20 0 0 0 0 30 20 Dead Dead main stem is dead, stump
sprout at base 34.152618 -117.873918
512 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 30 Poor Poor 34.152618 -117.873907 513 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 30 Fair Good 34.15253 -117.873984 514 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 15 Good Poor #514_#515 tagged on same tree 34.152501 -117.873898 515 0 #514_#515 tagged on same tree
516 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 25 15 Good Poor 34.152502 -117.873895 517 Phoenix canariensis Canary Island date palm Yes 27 1 27 0 0 0 0 30 20 Fair Good 34.152559 -117.873919 518 Phoenix canariensis Canary Island date palm Yes 27 1 27 0 0 0 0 50 20 Fair Good 34.152582 -117.873889 Item #8. Page 792
Meeting Date: 1/24/2023 / Packet Page #: 857
519 Phoenix canariensis Canary Island date palm Yes 27 1 27 0 0 0 0 45 15 Fair Good 34.152568 -117.873836 520 Phoenix canariensis Canary Island date palm Yes 27 1 27 0 0 0 0 30 15 Fair Fair 34.152561 -117.87381 521 Phoenix canariensis Canary Island date palm Yes 22 1 22 0 0 0 0 45 15 Fair Good 34.152561 -117.873762 522 Platauna racemosa California sycamore Yes 14 1 14 0 0 0 0 25 20 Fair Fair 34.152585 -117.873656 523 Phoenix canariensis Canary Island date palm Yes 24 1 24 0 0 0 0 30 15 Good Good 34.152659 -117.873792 524 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 14 10 Good Poor stump sprout 34.152731 -117.873624 525 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 15 20 Good Poor stump sprout 34.152731 -117.873623 526 Quercus agrifolia coast live oak Yes 47 4 47 0 0 0 0 45 35 Fair Poor 34.15278 -117.873668 527 Eucalyptus robusta swamp mahogany Yes 17 1 17 0 0 0 0 25 30 Good Poor 34.152772 -117.87363 528 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 20 12 Good Poor 34.152831 -117.873702 529 Juglans californica
Southern California black
walnut Yes 12 1 12 0 0 0 0 25 15 Fair Poor stump sprout 34.152843 -117.873705 530 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 15 Good Fair 34.152843 -117.873703 531 Phoenix canariensis Canary Island date palm Yes 11 1 11 0 0 0 0 30 18 Good Good 34.1529 -117.873356 532 Phoenix canariensis Canary Island date palm Yes 11 1 11 0 0 0 0 30 18 Good Good 34.152818 -117.873226 533 Quercus agrifolia coast live oak No 11 1 11 0 0 0 0 20 5 Dead Dead main stem is dead, stump
sprout at base 34.152816 -117.873224
534 Quercus agrifolia coast live oak Yes 62 1 62 0 0 0 0 45 45 Poor Fair 34.15298 -117.872929 535 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 10 Fair Fair 34.152997 -117.87297 536 Quercus agrifolia coast live oak Yes 26 1 26 0 0 0 0 35 30 Fair Fair 34.153081 -117.872978 537 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 50 30 Good Fair 34.153094 -117.87301 538 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 20 Fair Fair 34.153115 -117.873034 539 Washingtonia robusta Mexican fan palm Yes 11 1 11 0 0 0 0 30 15 Good Good 34.153179 -117.872947 540 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 55 15 Good Fair 34.153193 -117.872953 541 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 30 30 Fair Fair 34.153131 -117.872991 542 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 25 20 Poor Fair 34.153183 -117.873052 543 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 20 30 Fair Poor 34.153267 -117.873064 544 Quercus agrifolia coast live oak Yes 46 5 46 0 0 0 0 50 30 Poor Poor 34.153298 -117.873141 545 Quercus agrifolia coast live oak Yes 26 2 26 0 0 0 0 30 20 Fair Poor 34.153384 -117.873104 546 Quercus agrifolia coast live oak No 19 1 19 0 0 0 0 30 10 Dead Dead 34.1534 -117.873087 547 Quercus agrifolia coast live oak Yes 37 2 37 0 0 0 0 35 30 Fair Poor 34.153459 -117.873105 548 Quercus agrifolia coast live oak Yes 15 2 15 0 0 0 0 25 20 Fair Poor 34.153454 -117.873159 549 Quercus agrifolia coast live oak Yes 40 2 40 0 0 0 0 40 25 Fair Poor 34.153453 -117.873163 550 Quercus agrifolia coast live oak Yes 24 2 24 0 0 0 0 30 20 Fair Poor 34.153477 -117.873148 551 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.153504 -117.873165 552 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 20 15 Fair Poor 34.153504 -117.873166 553 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 20 Fair Poor 34.1535 -117.873202 554 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 30 20 Fair Poor 34.153506 -117.8732 555 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 10 0 Dead Dead 34.153509 -117.873209 556 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 25 20 Poor Fair 34.153535 -117.87323 557 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Fair Fair 34.153587 -117.873226 558 Quercus agrifolia coast live oak Yes 35 2 35 0 0 0 0 35 25 Fair Fair 34.153554 -117.873136 559 Quercus agrifolia coast live oak No 10 1 10 0 0 0 0 12 5 Dead Dead 34.153585 -117.873129 560 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 20 15 Poor Poor 34.153596 -117.873124 561 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 30 20 Poor Poor 34.153692 -117.873233 562 Quercus agrifolia coast live oak Yes 27 1 27 0 0 0 0 50 30 Fair Fair 34.15375 -117.873278 563 Platanus racemosa California sycamore Yes 11 1 11 0 0 0 0 25 20 Poor Poor 34.153751 -117.87328 564 Juglans californica
Southern California
black walnut Yes 8 1 8 0 0 0 0 20 15 Poor Poor
main stem is dead, stump
sprout at base 34.153751 -117.873245
Item #8. Page 793
Meeting Date: 1/24/2023 / Packet Page #: 858
565 Platanus racemosa California sycamore No 16 1 16 0 0 0 0 25 15 Dead Dead main stem is dead, stump
sprout at base 34.153752 -117.873244
566 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 45 30 Poor Poor 34.153778 -117.873142 567 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 30 20 Poor Poor 34.153793 -117.873145 568 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 15 Poor Poor 34.153808 -117.873148 569 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 15 Fair Poor 34.153816 -117.873174 570 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 10 6 Fair Poor 34.153878 -117.87319 571 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 15 Fair Fair 34.153856 -117.87324 572 Juglans californica
Southern California black
walnut Yes 11 1 11 0 0 0 0 20 30 Good Poor stump sprout 34.153903 -117.8732 573 Quercus agrifolia coast live oak Yes 31 1 31 0 0 0 0 45 35 Fair Fair 34.153906 -117.873135 574 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 45 30 Fair Fair 34.153917 -117.873108 575 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 35 Fair Fair 34.15394 -117.87311 576 Platanus racemosa California sycamore No 13 1 13 0 0 0 0 20 0 Dead Dead 34.153955 -117.873099 577 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Fair 34.154033 -117.873125 578 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Good 34.154045 -117.873128 579 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 25 15 Fair Poor 34.154123 -117.873128 580 Quercus agrifolia coast live oak Yes 28 4 28 0 0 0 0 25 30 Fair Poor 34.154149 -117.873116 581 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 15 Fair Poor 34.154167 -117.873051 582 Platanus racemosa California sycamore No 30 1 30 0 0 0 0 0 0 Dead Dead laying on ground 34.15411 -117.872984 583 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 35 30 Poor Poor 34.154061 -117.872914 584 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 20 Fair Poor 34.154173 -117.873004 585 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 45 30 Poor Fair 34.154161 -117.87295 586 Juglans californica
Southern California black
walnut Yes 11 2 11 0 0 0 0 15 15 Fair Poor 34.154035 -117.87289 587 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 30 Fair Poor 34.15399 -117.872878 588 Quercus agrifolia coast live oak Yes 45 2 45 0 0 0 0 40 30 Good Fair 34.153863 -117.872928 589 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 15 Fair Fair 34.15376 -117.872995 590 Juglans californica Southern California Yes 15 2 15 0 0 0 0 20 30 Poor Poor 34.153737 -117.873001 591 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 30 Good Fair 34.153674 -117.872931 592 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 20 Fair Poor 34.153566 -117.872991 593 Juglans californica
Southern California black
walnut Yes 8 1 8 0 0 0 0 15 20 Good Poor 34.153608 -117.87297 594 Platanus racemosa California sycamore Yes 20 1 20 0 0 0 0 45 30 Fair Poor 34.153522 -117.872964 595 Quercus agrifolia coast live oak Yes 37 4 37 0 0 0 0 45 40 Fair Fair 34.153203 -117.872798 596 Quercus agrifolia coast live oak No 25 1 25 0 0 0 0 0 0 Dead Dead main stem is dead, stump
sprout at base 34.153017 -117.872626
597 Olea europaea fruitless olive Yes 10 1 10 0 0 0 0 12 12 Good Poor 34.153072 -117.872792 598 Quercus agrifolia coast live oak Yes 37 2 37 0 0 0 0 45 30 Poor Poor 34.152975 -117.872707 599 Olea europaea fruitless olive Yes 17 2 17 0 0 0 0 15 15 Good Poor stump sprout 34.153003 -117.872647 600 Olea europaea fruitless olive Yes 13 2 13 0 0 0 0 12 15 Good Poor 34.152969 -117.872716 601 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 45 15 Poor Poor behind fence on adjacent
property, no tag 34.150671 -117.872954
602 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 20 15 Poor Poor behind fence on adjacent
property, no tag 34.151077 -117.873176
603 Juglans californica
Southern California black
walnut No 4 4 4 0 0 0 0 15 15 Fair Poor stems of 3,2,2 34.151701 -117.873417 604 Olea europaea fruitless olive Yes 15 2 8 7 0 0 0 25 20 Fair Fair 34.151806 -117.873834 607 Platanus racemosa California sycamore No 9 4 5 4 0 0 0 15 18 Fair Poor stems of 3,3 34.152172 -117.874606 608 Juglans regia English walnut Yes 11 2 6 5 0 0 0 20 15 Fair Fair 34.152226 -117.874961 609 Platanus racemosa California sycamore No 0 4 0 0 0 0 0 10 15 Fair Poor stems of 3,3,2,2 34.152342 -117.874945 610 Platanus racemosa California sycamore Yes 16 4 4 4 4 4 0 15 15 Fair Poor 34.152358 -117.87523 611 Juglans regia English walnut No 0 4 0 0 0 0 0 20 15 Fair Poor stems of 3,3,3,2 34.152336 -117.875387 Item #8. Page 794
Meeting Date: 1/24/2023 / Packet Page #: 859
612 Platanus racemosa California sycamore Yes 18 4 6 4 4 4 0 25 15 Fair Poor 34.152498 -117.875345 613 Platanus racemosa California sycamore No 0 3 0 0 0 0 0 25 10 Fair Poor stems of 3,3,2 34.152447 -117.875411 614 Quercus agrifolia coast live oak No 5 1 5 0 0 0 0 16 10 Fair Fair 34.152386 -117.875517 615 Pittosporum undulatum Victorian box Yes 21 9 5 4 4 4 4 20 15 Fair Poor additional stems of 3, 5, 4, 4 34.152209 -117.875452 616 Quercus agrifolia coast live oak Yes 42 2 21 21 0 0 0 35 30 Poor Poor 34.15222 -117.875404 617 Quercus agrifolia coast live oak Yes 49 2 25 24 0 0 0 45 30 Poor Poor 34.152215 -117.87541 618 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 55 40 Poor Fair 34.152191 -117.875312 619 Quercus agrifolia coast live oak Yes 38 1 38 0 0 0 0 60 50 Fair Fair 34.152187 -117.875259 620 Quercus agrifolia coast live oak Yes 23 2 12 11 0 0 0 40 30 Fair Fair 34.152177 -117.875122 621 Schinus molle Peruvian pepper Yes 17 1 17 0 0 0 0 18 20 Fair Fair 34.15223 -117.87568 622 Citrus spp. citrus tree No 4 5 4 0 0 0 0 12 12 Fair Fair stems of 3,3,2,2 34.152269 -117.875763 623 Ficus benjamina weeping fig Yes 63 6 14 12 10 14 13 45 50 Fair Poor additional stem of 7 34.152185 -117.875776 624 Pinus pinea Italian stone pine Yes 25 1 25 0 0 0 0 45 50 Fair Fair 34.152174 -117.875888 625 Citrus spp. citrus tree No 8 6 4 4 0 0 0 15 12 Fair Fair additional stems of 3,3,2, 2 34.152247 -117.875913 626 Cedrus atlantica 'glauca' blue atlas cedar Yes 16 3 6 5 5 0 0 30 15 Fair Poor 34.152072 -117.876108 627 Pinus pinea Italian stone pine Yes 38 1 38 0 0 0 0 60 40 Fair Poor 34.152047 -117.876152 629 Citrus spp. citrus tree Yes 12 3 4 4 4 0 0 10 9 Fair Fair 34.152277 -117.875957 630 Citrus spp. citrus tree Yes 10 4 5 5 0 0 0 10 9 Fair Fair stem of 3 34.152304 -117.875912 631 Citrus spp. citrus tree Yes 18 3 9 5 4 0 0 10 9 Fair Fair 34.152325 -117.875849 632 Citrus spp. citrus tree No 9 4 5 4 0 0 0 10 9 Poor Poor stems of 3,3 34.152362 -117.875832 633 Citrus spp. citrus tree No 0 5 0 0 0 0 0 10 9 Poor Poor stems of 3,3,3,3,3 34.152368 -117.875817 634 Ficus benjamina weeping fig Yes 13 2 7 6 0 0 0 25 15 Good Poor 34.152465 -117.875872 635 Schinus terebinthifolia Brazilian pepper No 4 4 4 0 0 0 0 10 6 Poor Poor stems of 3,3,3 34.15257 -117.875812 636 Schinus terebinthifolia Brazilian pepper Yes 14 4 8 6 0 0 0 20 20 Fair Poor stems of 3,3 34.152585 -117.875801 637 Washingtonia robusta Mexican fan palm Yes 17 1 17 0 0 0 0 55 12 Fair Fair 34.152742 -117.876043 641 Quercus agrifolia coast live oak Yes 15 2 9 6 0 0 0 30 18 Fair Fair 34.15287 -117.876106 642 Olea europaea fruitless olive No 0 5 0 0 0 0 0 15 18 Fair Poor stems of 3,2,1,1,1 34.153047 -117.876171 643 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 15 Poor Poor 34.153006 -117.87618 644 Washingtonia robusta Mexican fan palm Yes 14 1 14 0 0 0 0 65 12 Poor Fair 34.153 -117.876262 645 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 18 15 Poor Poor 34.152989 -117.876269 646 Quercus agrifolia coast live oak Yes 18 3 9 5 4 0 0 25 15 Fair Poor 34.152993 -117.876316 647 Quercus agrifolia coast live oak Yes 19 2 11 8 0 0 0 20 15 Fair Poor 34.152964 -117.876346 648 Quercus agrifolia coast live oak Yes 14 3 10 4 0 0 0 15 12 Poor Poor stem of 3 34.152932 -117.876346 649 Quercus agrifolia coast live oak Yes 18 2 10 8 0 0 0 15 10 Poor Poor 34.152903 -117.876357 650 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Poor Poor 34.152895 -117.876375 651 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 10 Poor Poor 34.15289 -117.876372 652 Quercus agrifolia coast live oak Yes 16 2 9 7 0 0 0 25 10 Poor Poor 34.152861 -117.876405 653 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 12 Fair Poor 34.15282 -117.876388 654 Quercus agrifolia coast live oak Yes 17 2 9 8 0 0 0 10 8 Poor Poor 34.15288 -117.876457 655 Quercus agrifolia coast live oak Yes 24 2 14 10 0 0 0 25 10 Fair Poor 34.15288 -117.876458 656 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 10 8 Fair Poor broke trunk 34.152884 -117.876492 657 Quercus agrifolia coast live oak Yes 32 4 12 7 7 6 0 18 15 Fair Poor 34.152923 -117.87655 658 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 8 8 Fair Poor 34.152947 -117.87652 659 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 25 10 Poor Poor 34.153133 -117.87663 660 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 12 8 Poor Poor 34.153153 -117.876607 661 Quercus agrifolia coast live oak Yes 18 2 10 8 0 0 0 25 10 Poor Poor 34.153155 -117.876627 662 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 10 10 Poor Poor 34.153157 -117.876694 666 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 18 Fair Fair Steep, no access estimated dbh 34.153892 -117.876433 Item #8. Page 795
Meeting Date: 1/24/2023 / Packet Page #: 860
667 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 18 Fair Fair Steep, no access estimated dbh 34.153869 -117.876367 669 Quercus agrifolia coast live oak Yes 14 0 6 8 0 0 0 20 15 Poor Poor 34.15317 -117.876432 670 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Poor Poor 34.153134 -117.876419 671 Olea europaea fruitless olive Yes 56 5 21 13 9 6 7 20 10 Poor Poor 34.153085 -117.87643 672 Quercus agrifolia coast live oak Yes 13 2 8 5 0 0 0 20 8 Fair Poor 34.153078 -117.876405 673 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.153078 -117.876388 674 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 15 8 Fair Poor 34.153106 -117.876357 675 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 25 20 Poor Poor 34.153074 -117.876299 676 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 15 Poor Poor 34.153044 -117.876301 677 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Poor Fair 34.15318 -117.876321 678 Quercus agrifolia coast live oak Yes 24 1 7 11 6 0 0 30 20 Fair Poor 34.153211 -117.876297 679 Quercus agrifolia coast live oak Yes 24 1 7 11 6 0 0 30 20 Fair Poor 34.153362 -117.8763 679 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 15 Poor Poor Steep, no tag, estimate dbh 34.153447 -117.876492 680 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 35 Fair Fair Steep, no tag, estimate dbh 34.153456 -117.876435 681 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 45 35 Fair Fair Steep, no tag, estimate dbh 34.153454 -117.876399 682 Quercus agrifolia coast live oak Yes 22 2 16 6 0 0 0 50 30 Fair Fair Steep, no tag, estimate dbh 34.153477 -117.876414 683 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair Steep, no tag, estimate dbh 34.153519 -117.876426 684 Quercus agrifolia coast live oak Yes 28 2 14 14 0 0 0 25 30 Poor Fair Steep, no tag, estimate dbh 34.153525 -117.876399 685 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 15 15 Fair Poor 34.153704 -117.876303 686 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 15 Fair Fair 34.153658 -117.876226 687 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 10 10 Fair Poor sprout off fallen tree no tag
access 34.153714 -117.876144
688 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 17 12 Fair Fair Steep, no tag, estimate dbh 34.153846 -117.876307 689 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 10 18 Fair Poor 34.153828 -117.876292 690 Quercus agrifolia coast live oak Yes 12 1 7 5 0 0 0 15 18 Fair Poor 34.153842 -117.876236 691 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 6 Poor Poor Steep, no tag, estimate dbh 34.153742 -117.876126 692 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 25 15 Good Fair Steep, no tag, estimate dbh 34.153768 -117.876111 693 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 10 Fair Fair 34.153822 -117.876096 694 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 18 10 Poor Poor 34.153838 -117.876129 695 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 23 18 Fair Poor 34.153852 -117.876207 696 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.15388 -117.876145 697 Platanus racemosa California sycamore Yes 20 1 20 0 0 0 0 45 20 Poor Poor 34.15393 -117.876182 699 Juglans californica
Southern California black
walnut Yes 8 1 8 0 0 0 0 20 18 Good Fair Steep, no access estimated dbh 34.154082 -117.876273 700 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 18 Fair Poor 34.15399 -117.876173 701 Juglans californica
Southern California black
walnut Yes 9 1 9 0 0 0 0 20 15 Fair Poor no tag, couldn't access 34.154056 -117.876118 702 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 15 Fair Fair 34.154095 -117.876137 703 Quercus agrifolia coast live oak Yes 26 2 13 13 0 0 0 30 30 Fair Poor 34.154158 -117.876146 704 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 45 20 Fair Poor no tag, couldn't access 34.15416 -117.876152 707 Juglans californica
Southern California
black walnut No 0 5 0 0 0 0 0 12 10 Poor Fair
no tag, couldn't access, stems
estimated at 3,2,1,1,1 34.154169 -117.876044
708a Platanus racemosa California sycamore Yes 11 1 11 0 0 0 0 30 10 Poor Poor 34.154152 -117.876163 708b Juglans californica
Southern California black
walnut Yes 9 4 5 4 0 0 0 10 10 Fair Poor
no tag, couldn't access, stems of
3,2 34.153741 -117.875946
Item #8. Page 796
Meeting Date: 1/24/2023 / Packet Page #: 861
709 Juglans californica
Southern California black
walnut No 0 5 0 0 0 0 0 9 9 Fair Fair
no tag, couldn't access, stems of
3,3,2,2,2 34.153839 -117.875768
710 Juglans californica
Southern California
black walnut No 7 3 7 0 0 0 0 11 11 Poor Poor
no tag, couldn't access, stems
of 2,2 34.153961 -117.875821
711 Juglans californica Southern California Yes 24 3 9 7 8 0 0 25 20 Poor Poor no tag, couldn't access 34.153412 -117.875994 712 Juglans californica Southern California Yes 16 2 9 7 0 0 0 25 15 Poor Poor no tag, couldn't access 34.153514 -117.876049 713 Quercus agrifolia coast live oak No 0 4 0 0 0 0 0 15 10 Fair Poor stump sprout, stems of 2,2,2,1 34.15341 -117.876049 714 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 25 10 Fair Fair 34.152602 -117.875217 715 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 15 10 Fair Fair 34.15262 -117.87521 716 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 15 6 Fair Poor 34.152624 -117.875216 717 Platanus racemosa California sycamore No 0 2 0 0 0 0 0 18 10 Fair Poor stems of 3,2 34.152441 -117.874079 718 Platanus racemosa California sycamore No 0 5 0 0 0 0 0 15 12 Fair Poor stems of 3,3,2,2,2 34.152335 -117.874007 719 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 25 20 Fair Fair 34.150829 -117.872622 720 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 25 20 Fair Fair 34.150796 -117.872626 721 Quercus agrifolia coast live oak Yes 12 5 4 4 4 0 0 20 10 Fair Fair stems of 3,3 34.150927 -117.872632 722 Grevillea robusta silk oak Yes 10 2 5 5 0 0 0 30 23 Fair Fair 34.151096 -117.872629 723 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 20 Fair Fair 34.151289 -117.872646 724 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Poor Fair 34.151299 -117.872648 725 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 25 10 Poor Fair 34.151296 -117.872638 726 Quercus agrifolia coast live oak Yes 11 2 7 4 0 0 0 20 10 Poor Poor 34.15131 -117.872645 727 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 25 10 Fair Poor 34.151339 -117.872644 728 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.15135 -117.872639 729 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 20 10 Fair Poor 34.151375 -117.872627 730 Quercus agrifolia coast live oak Yes 14 2 7 7 0 0 0 18 22 Fair Fair 34.151395 -117.872653 731 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 15 8 Fair Poor 34.151424 -117.87265 732 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 15 Poor Fair 34.151452 -117.872658 733 Olea europaea fruitless olive No 7 3 7 0 0 0 0 15 20 Fair Poor stems of 3,2 34.151467 -117.872681 734 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 15 Fair Fair 34.151476 -117.872682 735 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 10 Fair Fair 34.151501 -117.87267 736 Schinus molle Peruvian pepper Yes 27 5 8 9 6 4 0 15 15 Fair Poor stem of 3 34.15201 -117.87305 737 Ficus elastica rubber tree Yes 34 1 34 0 0 0 0 25 25 Good Fair 34.152164 -117.873453 738 Ceratonia siliqua carob tree No 0 5 0 0 0 0 0 18 20 Fair Poor stems of 3,3,3,3,3 34.152165 -117.87357 739 Olea europaea fruitless olive No 0 5 0 0 0 0 0 20 20 Fair Poor stems of 3,3,3,3,3 34.152364 -117.87332 740 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 15 Fair Poor 34.152426 -117.87381 741 Quercus agrifolia coast live oak No 5 2 5 0 0 0 0 30 10 Fair Poor stem of 3 34.152661 -117.874751 742 Quercus agrifolia coast live oak No 4 2 4 0 0 0 0 20 5 Fair Poor stem of 3 34.152657 -117.874788 743 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 25 8 Fair Poor 34.152659 -117.874791 744 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 35 15 Fair Poor 34.152733 -117.87478 745 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 10 Fair Poor 34.152762 -117.874743 746 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 15 5 Poor Poor 34.152736 -117.874742 747 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 15 7 Poor Poor 34.152775 -117.874716 748 Quercus agrifolia coast live oak No 4 2 4 0 0 0 0 18 8 Fair Poor stem of 3 34.152842 -117.874771 749 Platanus racemosa California sycamore Yes 12 2 6 6 0 0 0 30 15 Fair Fair no tag, couldn't access 34.153071 -117.874703 750 Juglans californica
Southern California black
walnut Yes 8 2 4 4 0 0 0 20 18 Fair Fair no tag, couldn't access 34.15296 -117.874721 751 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 15 10 Fair Fair 34.153116 -117.874669 752 Juglans californica
Southern California black
walnut Yes 9 1 9 0 0 0 0 12 15 Fair Poor stump sprout 34.153204 -117.874846 753 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 13 9 Fair Poor 34.153357 -117.875034 754 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 12 Fair Fair 34.153384 -117.875125 Item #8. Page 797
Meeting Date: 1/24/2023 / Packet Page #: 862
755 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 15 8 Poor Fair 34.153401 -117.875127 756 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 12 Fair Fair no tag, couldn't access 34.153611 -117.874851 757 Juglans californica
Southern California black
walnut No 6 1 6 0 0 0 0 20 12 Fair Fair Steep, no tag, estimated dbh 34.153796 -117.874679 758 Juglans californica
Southern California black
walnut Yes 18 3 6 6 6 0 0 30 15 Fair Fair Steep, no tag, estimated dbh 34.153759 -117.874611 759 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 30 15 Fair Fair Steep, no tag, estimated dbh 34.153778 -117.874627 760 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 30 15 Fair Fair Steep, no tag, estimated dbh 34.153791 -117.874643 761 Platanus racemosa California sycamore No 6 1 6 0 0 0 0 30 15 Fair Fair Steep, no tag, estimated dbh 34.153908 -117.874693 762 Juglans californica
Southern California black
walnut No 4 1 4 0 0 0 0 30 15 Fair Fair Steep, no tag, estimated dbh 34.153946 -117.874666 763 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 15 Fair Fair Steep, no tag, estimated dbh 34.153962 -117.87461 764 Juglans californica
Southern California black
walnut No 7 7 7 0 0 0 0 30 20 Fair Poor
Steep, no tag, estimated dbh,
stems of 3,3,3,3 34.153873 -117.874553
766 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 20 10 Fair Fair Steep, no tag, estimated dbh 34.153825 -117.874565 767 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 15 Fair Poor 34.153522 -117.874702 768 Juglans californica
Southern California black
walnut No 0 5 0 0 0 0 0 18 20 Fair Poor stems of 3,3,3,3,3 34.15357 -117.874594 769 Platanus racemosa California sycamore Yes 15 2 10 5 0 0 0 30 10 Poor Poor 34.153538 -117.874503 770 Juglans californica
Southern California black
walnut No 0 3 0 0 0 0 0 20 40 Good Poor Stump regrowth, stems of 3,3,3 34.153107 -117.874526 771 Juglans californica
Southern California black
walnut Yes 16 4 4 4 4 4 0 20 40 Good Poor Stump regrowth 34.153129 -117.874516 772 Quercus agrifolia coast live oak Yes 32 3 11 11 10 0 0 30 20 Fair Poor no tag, couldn't access 34.153024 -117.87434 773 Juglans californica
Southern California black
walnut Yes 9 1 9 0 0 0 0 30 20 Good Poor no tag, couldn't access 34.153103 -117.874453 773 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 20 10 Fair Poor 34.152933 -117.874444 774 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 20 10 Fair Poor 34.152843 -117.874529 775 Juglans californica
Southern California black
walnut No 6 1 6 0 0 0 0 20 10 Fair Poor no tag, couldn't access 34.152929 -117.87459 775 Juglans californica
Southern California black
walnut No 6 1 6 0 0 0 0 20 10 Fair Poor no tag, couldn't access 34.152929 -117.87459 776 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 30 10 Fair Fair no tag, couldn't access 34.152934 -117.874605 777 Quercus agrifolia coast live oak No 0 4 0 0 0 0 0 15 15 Fair Poor stems of 3,2,2,2 34.152734 -117.874233 778 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 30 Fair Fair no tag, couldn't access 34.152935 -117.873896 779 Quercus agrifolia coast live oak No 0 4 0 0 0 0 0 11 7 Fair Poor stems of 3,2,2,2 34.152765 -117.873923 780 Platanus racemosa California sycamore No 9 5 5 4 0 0 0 25 20 Fair Poor stump sprout from fire, stems of
3,3,3 34.152644 -117.873672
781 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 10 Fair Fair 34.152839 -117.873108 782 Eucalyptus robusta swamp mahogny Yes 26 5 6 5 5 4 6 25 25 Fair Poor stump sprout 34.152832 -117.87311 783 Quercus agrifolia coast live oak No 0 3 0 0 0 0 0 12 12 Fair Poor stump sprout, stems of 2,2,2 34.152876 -117.873086 784 Quercus agrifolia coast live oak No 5 1 5 0 0 0 0 20 8 Fair Poor 34.153621 -117.873221 785 Quercus agrifolia coast live oak No 5 1 5 0 0 0 0 20 8 Fair Poor 34.153636 -117.873227 786 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 20 8 Fair Poor 34.153645 -117.873205 787 Juglans californica
Southern California black
walnut No 7 1 7 0 0 0 0 15 15 Good Poor 34.153674 -117.873281 788 Quercus agrifolia coast live oak No 5 1 5 0 0 0 0 17 5 Fair Poor 34.15365 -117.873178 789 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 10 7 Fair Poor 34.153777 -117.873149 790 Quercus agrifolia coast live oak No 4 2 4 0 0 0 0 10 7 Fair Poor stems of 2,2 34.153795 -117.873093 791 Quercus agrifolia coast live oak No 4 2 4 0 0 0 10 2 Poor Poor stem of 3 34.154004 -117.873126 792 Quercus agrifolia coast live oak No 7 1 7 0 0 0 0 18 10 Fair Fair 34.154073 -117.873165 Item #8. Page 798
Meeting Date: 1/24/2023 / Packet Page #: 863
793 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 35 15 Fair Fair 34.154194 -117.873197 793 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 15 8 Fair Poor no tag, couldn't access 34.153889 -117.873497 795 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 12 10 Poor Poor 34.153876 -117.873101 796 Quercus agrifolia coast live oak Yes 10 0 10 0 0 0 0 45 18 Fair Fair no tag, couldn't access 34.153769 -117.872557 797 Juglans californica
Southern California black
walnut Yes 10 0 10 0 0 0 0 30 30 Fair Fair no tag, couldn't access 34.15352 -117.872542 798 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 15 Poor Poor 34.153254 -117.872672 800 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 25 12 Poor Poor 34.152791 -117.872535 801 Quercus agrifolia coast live oak No 5 1 5 0 0 0 0 9 3 Poor Poor 34.152656 -117.872585 802 Quercus agrifolia coast live oak Yes 8 2 4 4 0 0 0 8 1 Poor Poor 34.152602 -117.87257 803 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 8 Fair Poor located on adjacent property, did
not tag 34.152516 -117.872554
804 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 35 15 Fair Fair located on adjacent property, did
not tag 34.152507 -117.872554
805 Quercus agrifolia coast live oak Yes 44 2 28 16 0 0 0 40 20 Fair Fair located on adjacent property, did
not tag 34.152507 -117.872554
806 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 25 Fair Fair located on adjacent property, did
not tag 34.152425 -117.872583
807 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 10 Fair Fair 34.152273 -117.872595 808 Quercus agrifolia coast live oak No 6 1 6 0 0 0 0 20 10 Fair Fair 34.152262 -117.872603 809 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 10 Fair Poor 34.152241 -117.872602 810 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 18 15 Fair Fair 34.152154 -117.872632 811 Quercus agrifolia coast live oak Yes 10 2 5 5 0 0 0 20 15 Poor Fair 34.152052 -117.872663 812 Quercus agrifolia coast live oak Yes 10 2 5 5 0 0 0 12 10 Fair Poor 34.152002 -117.872674 813 Schinus molle Peruvian pepper Yes 24 5 10 9 5 0 0 20 20 Fair Fair stems of 3,3 34.152037 -117.872593 814 Schinus molle Peruvian pepper Yes 33 5 10 8 6 5 4 20 20 Fair Fair 34.152086 -117.872561 815 Quercus agrifolia coast live oak Yes 18 2 9 9 0 0 0 15 10 Poor Poor 34.152089 -117.87257 816 Quercus agrifolia coast live oak No 4 1 4 0 0 0 0 15 8 Fair Fair 34.152103 -117.872555 817 Schinus molle Peruvian pepper Yes 16 2 8 8 0 0 0 15 20 Fair Poor 34.152142 -117.872577 818 Schinus molle Peruvian pepper Yes 16 2 8 8 0 0 0 15 20 Fair Poor 34.151958 -117.87268 819 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 25 30 Fair Fair 34.15186 -117.872617 820 Quercus agrifolia coast live oak Yes 8 4 4 4 0 0 0 25 15 Fair Poor stems of 3,3 34.15189 -117.872611 821 Schinus molle Peruvian pepper Yes 35 3 12 12 11 0 0 25 10 Fair Poor 34.15185 -117.872584 822 Schinus molle Peruvian pepper Yes 34 2 12 12 10 0 0 30 15 Poor Poor 34.151734 -117.872653 823 Quercus agrifolia coast live oak Yes 21 5 6 5 5 5 0 25 15 Fair Poor stem of 3 34.151735 -117.872634 824 Quercus agrifolia coast live oak Yes 21 3 8 6 7 0 0 35 15 Fair Poor 34.151751 -117.872561 825 Quercus agrifolia coast live oak No 0 5 0 0 0 0 0 12 10 Fair Poor stems of 3,3,2,2,2 34.151766 -117.872565 826 Quercus agrifolia coast live oak Yes 13 5 5 4 4 0 0 25 15 Fair Poor stems of 2,2 34.151739 -117.872555 827 Quercus agrifolia coast live oak Yes 19 5 6 5 4 4 0 20 15 Fair Poor stem of 3 34.15171 -117.872556 828 Olea europaea fruitless olive Yes 36 5 14 9 8 5 0 30 20 Fair Poor stem of 3 34.152233 -117.873084 829 Eucalyptus cladocalx sugar gum Yes 14 3 6 4 4 0 0 40 12 Fair Poor 34.152504 -117.873121 830 Eucalyptus cladocalx sugar gum Yes 16 5 3 4 5 4 0 40 12 Fair Poor stem of 3 34.152511 -117.873136 831 Eucalyptus cladocalx sugar gum Yes 11 2 6 5 0 0 0 40 18 Fair Poor 34.152533 -117.873146 832 Eucalyptus cladocalx sugar gum Yes 20 4 6 5 5 4 0 40 25 Fair Poor 34.152555 -117.873121 833 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Poor 34.152698 -117.872819 834 Quercus agrifolia coast live oak No 4 1 4 0 0 0 0 10 5 Poor Poor 34.152697 -117.872819 835 Olea europaea fruitless olive Yes 15 2 8 7 0 0 0 30 20 Fair Poor 34.152793 -117.872793 Item #8. Page 799
Meeting Date: 1/24/2023 / Packet Page #: 864
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
1 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 22 25 Fair Poor tree is topped, growing
under power lines 34.150459
-
117.87264
3 Casuarina
cunninghamiana river she-oak Yes 29 1 29 0 0 0 0 60 20 Good Good 34.150417 -
117.87273
4 Pinus canariensis
Canary Island
pine Yes 26 1 26 0 0 0 0 70 20 Good Poor 34.150429
-
117.87276
5 Jacaranda
mimosifolia jacaranda Yes 20 3 10 5 5 0 0 18 18 Fair Poor tree is topped, growing
under power lines 34.15048
-
117.87263
6 Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 90 15 Good Fair 34.150509
-
117.87297
7 Pinus canariensis
Canary Island
pine Yes 30 1 30 0 0 0 0 90 30 Good Fair 34.150649
-
117.87294
8 Casuarina
cunninghamiana river she-oak Yes 19 1 19 0 0 0 0 35 25 Fair Fair top of tree is dead 34.150678 -
117.87289
11 Jacaranda
mimosifolia jacaranda Yes 18 2 10 8 0 0 0 30 30 Fair Fair 34.150597 -
117.87272
12 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 18 Poor Fair 34.150632 -
117.87271
13 Quercus agrifolia coast live oak Yes 15 2 8 7 0 0 0 10 10 Fair Poor 34.150677 -
117.87271
14 Washingtonia
robusta
Mexican fan
palm Yes 11 1 11 0 0 0 0 75 15 Good Fair 34.150672
-
117.87273
16 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 10 Good Poor 34.15072 -
117.87266
17 Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 95 15 Good Fair 34.15072
-
117.87266
18 Washingtonia
robusta
Mexican fan
palm Yes 17 1 17 0 0 0 0 20 10 Good Good 34.150739
-
117.87267
19 Casuarina
cunninghamiana river she-oak Yes 14 1 14 0 0 0 0 50 20 Fair Good 34.150788 -
117.87266
20 Cedrus deodora deodar cedar Yes 20 1 20 0 0 0 0 50 30 Fair Fair 34.150746 -
117.87279
21 Phoenix canariensis
Canary Island
date palm Yes 20 1 20 0 0 0 0 60 20 Good Good 34.150766 -
117.87299
22 Cedrus deodora deodar cedar Yes 23 1 23 0 0 0 0 55 25 Fair Fair 34.150853 -
117.87299
24 Phoenix canariensis
Canary Island
date palm Yes 18 1 18 0 0 0 0 45 18 Good Good 34.150911 -
117.87309
25 Cedrus deodora deodar cedar Yes 17 1 17 0 0 0 0 40 20 Fair Fair 34.150973 -
117.87306
28 Casuarina
cunninghamiana river she-oak Yes 21 1 21 0 0 0 0 55 18 Fair Poor 34.150833 -
117.87274
29 Pinus canariensis
Canary Island
pine Yes 24 1 24 0 0 0 0 55 20 Fair Fair top of tree is dead 34.150877 -
117.87274
Item #8. Page 800
Meeting Date: 1/24/2023 / Packet Page #: 865
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
30 Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 40 10 Fair Good 34.150892
-
117.87262
31 Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 45 12 Good Good 34.150938
-
117.87261
32 Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 25 10 Good Good 34.150959
-
117.87261
33 Casuarina
cunninghamiana river she-oak Yes 15 1 15 0 0 0 0 35 20 Fair Fair top of tree is dead 34.150933 -
117.87275
34 Grevillea robusta silk oak Yes 22 1 22 0 0 0 0 50 20 Good Fair 34.150985 -
117.87273
35 Casuarina
cunninghamiana river she-oak Yes 15 1 15 0 0 0 0 35 15 Fair Fair top of tree is dead 34.150947 -
117.87279
36 Casuarina
cunninghamiana river she-oak Yes 18 1 18 0 0 0 0 50 20 Good Fair 34.150948 -
117.87286
37 Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 30 10 Fair Good 34.15109
-
117.87263
38 Casuarina
cunninghamiana river she-oak Yes 20 1 20 0 0 0 0 55 25 Good Fair 34.151083 -
117.87271
39 Grevillea robusta silk oak Yes 25 1 25 0 0 0 0 55 25 Poor Poor 34.151115 -
117.87275
40 Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 50 15 Good Good 34.151104
-
117.87283
41 Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 50 15 Good Good 34.151081
-
117.87285
42 Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 45 15 Good Poor 34.151076
-
117.87291
43 Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 55 12 Good Poor 34.151114
-
117.87288
44 Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 60 12 Good Fair 34.151178
-
117.87293
45 Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 60 12 Good Fair 34.151145
-
117.87297
46 Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 60 12 Good Fair 34.151209
-
117.87298
47 Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 60 12 Good Fair 34.151225
-
117.87291
48 Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 60 12 Good Fair 34.151255
-
117.87297
49 Phoenix canariensis
Canary Island
date palm Yes 20 1 20 0 0 0 0 25 15 Good Good 34.151237 -
117.87302
50 Phoenix canariensis
Canary Island
date palm Yes 21 1 21 0 0 0 0 30 20 Good Good 34.151175 -
117.87302
52 Cedrus deodora deodar cedar Yes 23 1 23 0 0 0 0 50 30 Fair Fair 34.151141 -
117.87308
Item #8. Page 801
Meeting Date: 1/24/2023 / Packet Page #: 866
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
53 Pinus canariensis
Canary Island
pine Yes 17 1 17 0 0 0 0 55 20 Fair Poor 34.151166
-
117.87274
54 Pinus canariensis
Canary Island
pine Yes 11 1 11 0 0 0 0 30 15 Fair Fair 34.151243 -117.8728 55 Pinus canariensis
Canary Island
pine Yes 27 1 27 0 0 0 0 70 30 Fair Fair 34.15127
-
117.87275
56 Pinus canariensis
Canary Island
pine Yes 21 1 21 0 0 0 0 70 30 Fair Fair 34.151273
-
117.87282
57 Pinus canariensis
Canary Island
pine Yes 20 1 20 0 0 0 0 70 20 Fair Fair 34.151293
-
117.87287
58 Pinus canariensis
Canary Island
pine Yes 17 1 17 0 0 0 0 60 15 Poor Fair 34.15133
-
117.87285
59 Pinus canariensis
Canary Island
pine Yes 19 1 19 0 0 0 0 65 15 Fair Poor 34.151334
-
117.87293
60 Pinus canariensis
Canary Island
pine Yes 22 1 22 0 0 0 0 70 20 Fair Fair 34.151296
-
117.87295
61 Pinus canariensis
Canary Island
pine Yes 22 1 22 0 0 0 0 65 20 Good Fair 34.151295
-
117.87307
62 Pinus canariensis
Canary Island
pine Yes 23 1 23 0 0 0 0 65 20 Fair Fair 34.15133
-
117.87312
63 Pinus canariensis
Canary Island
pine Yes 22 1 22 0 0 0 0 65 20 Poor Fair 34.151392
-
117.87311
64 Pinus canariensis
Canary Island
pine Yes 20 1 20 0 0 0 0 60 15 Fair Poor 34.151353
-
117.87303
65 Pinus canariensis
Canary Island
pine Yes 17 1 17 0 0 0 0 55 10 Poor Poor 34.151381
-
117.87303
66 Pinus canariensis
Canary Island
pine Yes 12 1 12 0 0 0 0 40 10 Fair Poor 34.151408
-
117.87308
67 Pinus canariensis
Canary Island
pine Yes 20 1 20 0 0 0 0 60 15 Fair Fair 34.151403
-
117.87295
68 Pinus canariensis
Canary Island
pine Yes 21 1 21 0 0 0 0 60 15 Fair Fair 34.15139
-
117.87289
69 Pinus canariensis
Canary Island
pine Yes 22 1 22 0 0 0 0 60 15 Fair Fair 34.151435
-
117.87294
70 Pinus canariensis
Canary Island
pine Yes 23 1 23 0 0 0 0 60 15 Fair Fair 34.15143
-
117.87298
71 Pinus canariensis
Canary Island
pine Yes 19 1 19 0 0 0 0 75 15 Fair Fair 34.151476
-
117.87301
72 Pinus canariensis
Canary Island
pine Yes 20 1 20 0 0 0 0 75 15 Fair Fair 34.151505
-
117.87296
73 Pinus canariensis
Canary Island
pine Yes 22 1 22 0 0 0 0 75 20 Fair Poor 34.151498
-
117.87286
74 Pinus canariensis
Canary Island
pine Yes 22 1 22 0 0 0 0 70 15 Fair Poor 34.151557 -117.8729 76 Eucalyptus robusta
swamp
mahogany Yes 15 1 15 0 0 0 0 15 20 Good Poor 34.15157
-
117.87294
Item #8. Page 802
Meeting Date: 1/24/2023 / Packet Page #: 867
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
77 Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 30 12 Good Good 34.151731
-
117.87302
78 Olea europaea fruitless olive Yes 12 1 12 0 0 0 0 20 20 Good Fair 34.151655 -
117.87304
79 Quercus agrifolia coast live oak Yes 26 4 9 9 4 4 0 20 20 Good Fair 34.151621 -
117.87287
80 Heteromeles
arbutifolia toyon Yes 21 5 7 5 5 4 0 15 15 Poor Fair 34.151508 -
117.87307
82 Grevillea robusta silk oak Yes 24 1 24 0 0 0 0 65 30 Fair Fair 34.15155 -
117.87312
83 Olea europaea fruitless olive Yes 26 3 10 10 6 0 0 30 30 Good Poor 34.151585 -117.8731 84 Grevillea robusta silk oak Yes 18 1 18 0 0 0 0 55 20 Fair Fair 34.151607 -
117.87315
86 Grevillea robusta silk oak Yes 20 1 20 0 0 0 0 55 15 Good Good 34.15167 -
117.87315
87 Grevillea robusta silk oak Yes 19 1 19 0 0 0 0 50 15 Fair Fair 34.151595 -
117.87322
88 Grevillea robusta silk oak Yes 16 1 16 0 0 0 0 45 15 Fair Fair 34.151534 -
117.87318
90 Cedrus deodora deodar cedar Yes 26 1 26 0 0 0 0 55 30 Fair Fair 34.151316 -
117.87316
91 Grevillea robusta silk oak Yes 11 1 11 0 0 0 0 40 15 Good Fair 34.151366 -
117.87316
94 Casuarina
cunninghamiana river she-oak Yes 14 1 14 0 0 0 0 35 15 Fair Fair 34.151415 -117.8732 96 Olea europaea fruitless olive Yes 20 2 10 10 0 0 0 30 30 Good Fair 34.151449 -
117.87328
102 Cedrus deodora deodar cedar Yes 31 1 31 0 0 0 0 65 30 Fair Good 34.151757 -
117.87357
103 Arucaria bidwillii bunya-bunya Yes 20 1 20 0 0 0 0 55 20 Fair Fair 34.151827 -
117.87346
104 Arucaria bidwillii bunya-bunya Yes 16 1 16 0 0 0 0 55 15 Fair Fair 34.151884 -117.8735 107 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 30 35 Good Fair 34.151819 -
117.87401
108 Quercus agrifolia coast live oak Yes 36 1 36 0 0 0 0 35 40 Good Poor 34.151867 -
117.87416
109 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 35 30 Good Fair 34.151924 -
117.87438
110 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 15 Good Fair 34.15193 -117.8744 111 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 25 20 Good Fair 34.152112 -
117.87457
112 Quercus agrifolia coast live oak Yes 35 1 35 0 0 0 0 45 40 Good Fair 34.152039 -
117.87461
113 Cedrus deodora deodar cedar Yes 11 1 11 0 0 0 0 45 15 Fair Fair 34.152157 -
117.87472
Item #8. Page 803
Meeting Date: 1/24/2023 / Packet Page #: 868
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
115
Pseudotsaya
menziesii Douglas-fir Yes 12 1 12 0 0 0 0 40 8 Poor Poor 34.1522 -
117.87487
116 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 25 Good Fair 34.15222 -
117.87506
117 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 20 Good Fair 34.15225 -
117.87519
119 Phoenix canariensis
Canary Island
date palm Yes 23 1 23 0 0 0 0 35 20 Good 34.152379
-
117.87449
120 Phoenix canariensis
Canary Island
date palm Yes 17 1 17 0 0 0 0 30 15 Good Fair 34.152361 -
117.87446
121 Phoenix canariensis
Canary Island
date palm Yes 20 1 20 0 0 0 0 40 15 Good Good 34.152427 -
117.87426
122 Phoenix canariensis
Canary Island
date palm Yes 20 1 20 0 0 0 0 40 15 Fair Good 34.152361 -
117.87427
123 Phoenix canariensis
Canary Island
date palm Yes 19 1 19 0 0 0 0 40 15 Fair Good 34.152323 -
117.87427
124
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152242
-
117.87553
125
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152308
-
117.87556
126
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.15228
-
117.87559
127
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152284
-
117.87565
128
Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152347
-
117.87556
129
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.15233
-
117.87564
130
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.15235
-
117.87568
131
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152386
-
117.87567
132
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152387
-
117.87571
133
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152429
-
117.87568
134
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152435
-
117.87574
135
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152484
-
117.87575
136
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152486
-
117.87572
137
Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152483
-
117.87568
138
Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152513 -117.8756 Item #8. Page 804
Meeting Date: 1/24/2023 / Packet Page #: 869
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
139
Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 55 15 Fair Fair shares tag with #172 34.152574 -
117.87561
140
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152521
-
117.87567
141
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152555
-
117.87574
142
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 80 15 Good Fair 34.152539
-
117.87578
143
Washingtonia
robusta
Mexican fan
palm Yes 17 1 17 0 0 0 0 80 15 Good Fair 34.152594
-
117.87584
144
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152624
-
117.87577
145
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 80 15 Good Fair 34.152657
-
117.87577
146
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 80 15 Good Fair 34.152668
-
117.87586
147
Washingtonia
robusta
Mexican fan
palm Yes 18 1 18 0 0 0 0 80 15 Good Fair 34.152681 -117.876 148
Washingtonia
robusta
Mexican fan
palm Yes 17 1 17 0 0 0 0 80 15 Good Fair 34.152678
-
117.87597
149 Quercus agrifolia coast live oak Yes 40 1 40 0 0 0 0 45 50 Good Good 34.15229 -
117.87556
150 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 20 Good Fair 34.152403 -
117.87566
151 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 45 35 Fair Good 34.152435 -
117.87564
152 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 25 20 Fair Fair 34.152446 -
117.87558
153 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Fair 34.152467 -
117.87568
154 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 25 20 Fair Fair 34.152484 -117.8757 157 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 50 35 Fair Fair 34.152548 -
117.87571
159 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 20 25 Fair Fair 34.152645 -
117.87576
160 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Fair 34.152724 -
117.87597
161 Quercus agrifolia coast live oak Yes 26 2 13 13 0 0 0 30 30 Fair Fair 34.152693 -
117.87599
162
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 60 15 Fair Fair 34.152747
-
117.87598
163 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 30 Fair Fair 34.152743 -
117.87596
166 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 40 35 Fair Fair 34.152706 -117.8758 168
Washingtonia
robusta
Mexican fan
palm Yes 13 1 13 0 0 0 0 80 15 Good Fair 34.152664
-
117.87566
Item #8. Page 805
Meeting Date: 1/24/2023 / Packet Page #: 870
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
169 Quercus agrifolia coast live oak Yes 29 2 15 14 0 0 0 30 30 Fair Poor 34.152625 -
117.87564
170 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 30 Fair Fair 34.152619 -
117.87559
171 Olea europaea fruitless olive Yes 20 2 10 10 0 0 0 30 25 Good Poor 34.152596 -
117.87561
173 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 45 30 Fair Fair 34.152496 -
117.87553
174 Pinus pinea
Italian stone
pine Yes 50 1 50 0 0 0 0 40 40 Fair Poor 34.152215
-
117.87601
175 Quercus agrifolia coast live oak Yes 20 2 11 9 0 0 0 20 20 Good Fair 34.152305 -
117.87601
179 Quercus agrifolia coast live oak Yes 35 1 35 0 0 0 0 35 35 Fair Fair laying on ground 34.152909 -
117.87279
180 Quercus agrifolia coast live oak Yes 30 1 30 0 0 0 0 40 25 Poor Poor 34.152865 -
117.87259
182 Quercus agrifolia coast live oak Yes 10 2 6 4 0 0 0 18 10 Fair Poor 34.152847 -
117.87254
183 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Fair Poor 34.152818 -
117.87257
184 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Poor 34.152793 -
117.87263
185 Quercus agrifolia coast live oak Yes 26 1 26 0 0 0 0 50 35 Fair Fair 34.152794 -
117.87268
186 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 45 30 Fair Fair 34.152731 -
117.87279
187 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 50 20 Fair Fair 34.152754 -
117.87272
188 Quercus agrifolia coast live oak Yes 32 1 32 0 0 0 0 55 35 Fair Fair 34.152749 -
117.87272
189 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 40 25 Fair Fair 34.152743 -
117.87264
190 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 10 Fair Fair 34.152723 -
117.87266
191 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Good Fair 34.15273 -
117.87258
192 Quercus agrifolia coast live oak Yes 30 1 30 0 0 0 0 45 35 Fair Fair 34.152757 -
117.87254
193 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 50 20 Fair Fair 34.152696 -
117.87258
194 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 40 25 Fair Fair 34.152692 -
117.87267
195 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 40 20 Fair Fair 34.152644 -
117.87257
196 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 35 25 Fair Fair 34.152644 -117.8726 198 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 35 20 Fair Fair 34.152631 -
117.87269
Item #8. Page 806
Meeting Date: 1/24/2023 / Packet Page #: 871
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
199 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Fair Fair 34.152606 -
117.87267
200 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 45 20 Good Fair 34.152587 -
117.87259
203 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 25 Fair Fair 34.152612 -117.8728 204 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 35 30 Fair Fair 34.152513 -
117.87269
205 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 40 40 Fair Fair 34.152471 -
117.87266
207 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 25 Fair Poor 34.152497 -
117.87268
211 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Fair Fair 34.152496 -
117.87279
212 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 10 Fair Fair 34.152484 -
117.87279
213 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 20 Good Fair 34.152463 -
117.87278
215 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 15 Good Fair 34.152475 -
117.87282
217 Quercus agrifolia coast live oak Yes 28 2 16 12 0 0 0 20 15 Good Fair 34.152459 -
117.87287
218 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.152392 -117.8727 219 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 8 Fair Poor 34.152384 -
117.87271
220 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Fair 34.152332 -
117.87276
221 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 13 Fair Fair 34.152318 -
117.87276
232 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 20 20 Fair Poor 34.152239 -
117.87283
235 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Fair Fair 34.152362 -
117.87264
238 Quercus agrifolia coast live oak Yes 38 3 12 13 13 0 0 30 30 Good Fair 34.152219 -117.8727 240 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 20 Fair Fair 34.152154 -
117.87285
242 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Poor 34.152165 -
117.87282
244 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 12 Fair Fair 34.152151 -117.8728 245 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 12 Fair Fair 34.152145 -117.8728 246 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 6 10 Fair Poor 34.152122 -
117.87284
248 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 15 10 Fair Fair 34.152085 -117.8728 255 Olea europaea fruitless olive Yes 22 2 22 0 0 0 0 35 25 Fair Fair 34.152769 -
117.87284
256 Olea europaea fruitless olive Yes 18 1 18 0 0 0 0 30 20 Fair Poor 34.152581 -
117.87274
Item #8. Page 807
Meeting Date: 1/24/2023 / Packet Page #: 872
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
257 Olea europaea fruitless olive Yes 22 3 22 0 0 0 0 20 15 Fair Poor 34.152295 -
117.87279
258 Olea europaea fruitless olive Yes 25 3 25 0 0 0 0 30 25 Fair Poor 34.152312 -
117.87268
259 Olea europaea fruitless olive Yes 14 3 14 0 0 0 0 15 15 Fair Poor 34.152327 -
117.87272
260 Olea europaea fruitless olive Yes 13 1 13 0 0 0 0 15 20 Poor Poor 34.152286 -
117.87269
261 Olea europaea fruitless olive Yes 16 2 16 0 0 0 0 15 15 Fair Poor 34.152322 -
117.87308
262 Olea europaea fruitless olive Yes 24 3 24 0 0 0 0 25 30 Fair Poor 34.152244 -
117.87305
263 Olea europaea fruitless olive Yes 50 5 10 10 10 10 10 25 30 Fair Poor 34.152031 -
117.87272
264 Olea europaea fruitless olive Yes 18 4 18 0 0 0 0 25 30 Good Poor 34.151664 -
117.87295
265 Olea europaea fruitless olive Yes 18 1 18 0 0 0 0 30 20 Good Poor 34.151654 -
117.87316
266 Ceratonia siliqua carob Yes 28 1 28 0 0 0 0 30 50 Fair Fair 34.15157 -
117.87331
270 Pinus canariensis
Canary Island
pine Yes 18 1 18 0 0 0 0 65 15 Poor Poor 34.152701
-
117.87549
272 Pinus canariensis
Canary Island
pine Yes 33 1 33 0 0 0 0 70 35 Fair Poor 34.152695
-
117.87543
273 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 30 Fair Fair 34.152693 -
117.87547
274 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 15 Fair Fair 34.152713 -
117.87538
275 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 15 Fair Poor 34.152691 -
117.87534
277 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 45 30 Good Fair 34.152598 -
117.87529
279 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 50 30 Fair Fair 34.152538 -
117.87516
280 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 20 Good Fair 34.152569 -
117.87508
281 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 50 30 Poor Fair 34.152535 -
117.87509
282 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 25 Fair Fair 34.152551 -
117.87503
283 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Poor 34.152544 -
117.87485
285 Quercus agrifolia coast live oak Yes 20 2 20 0 0 0 0 35 30 Fair Fair 34.152559 -
117.87457
288
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 75 15 Fair Fair 34.152826
-
117.87575
Item #8. Page 808
Meeting Date: 1/24/2023 / Packet Page #: 873
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
289
Washingtonia
robusta
Mexican fan
palm Yes 18 1 18 0 0 0 0 75 15 Fair Fair 34.152747
-
117.87594
290 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 20 20 Fair Fair 34.152748 -
117.87594
291
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 75 15 Fair Fair 34.152808
-
117.87592
292 Olea europaea fruitless olive Yes 24 2 24 0 0 0 0 20 15 Poor Poor 34.152835 -
117.87594
293
Washingtonia
robusta
Mexican fan
palm Yes 17 1 17 0 0 0 0 75 15 Fair Fair 34.15287
-
117.87594
294 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 30 30 Poor Poor 34.152909 -
117.87595
295 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 10 10 Fair Poor 34.15289 -117.876 296 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 20 20 Fair Fair 34.152847 -
117.87609
297 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Fair Fair 34.15286 -117.8761 298
Washingtonia
robusta
Mexican fan
palm Yes 15 1 15 0 0 0 0 75 15 Fair Fair 34.152765
-
117.87607
300 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 35 40 Fair Fair 34.152833 -
117.87624
303 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 6 4 Good Poor stump sprout 34.152896 -
117.87621
304 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 20 Poor Poor 34.152988 -
117.87618
307 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 15 10 Fair Fair 34.153127 -
117.87621
308 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.153161 -
117.87621
309 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 30 Fair Fair 34.153193 -
117.87623
310 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 15 Fair Fair 34.153132 -
117.87616
314 Corymbia maculata spotted gum Yes 38 1 38 0 0 0 0 90 45 Poor Poor 34.153041 -
117.87594
316 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 20 Poor Poor 34.152913 -
117.87585
318
Washingtonia
robusta
Mexican fan
palm Yes 10 1 10 0 0 0 0 75 15 Fair Fair 34.152814
-
117.87575
319 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 30 Fair Fair 34.153339 -
117.87631
320 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 20 Fair Fair 34.15333 -
117.87631
321 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 35 Fair Fair 34.153346 -117.8763 322 Quercus agrifolia coast live oak Yes 58 1 58 0 0 0 0 40 40 Fair Fair 34.153447 -
117.87635
Item #8. Page 809
Meeting Date: 1/24/2023 / Packet Page #: 874
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
323 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 15 Fair Fair 34.153473 -
117.87634
324 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 20 Fair Fair 34.153447 -
117.87629
325 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Fair Fair 34.153514 -
117.87632
326 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Fair Fair 34.153513 -
117.87632
327 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 20 Fair Fair 34.153639 -
117.87622
328 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 20 Fair Fair 34.153665 -
117.87627
329 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 35 30 Fair Fair 34.153496 -
117.87626
330 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 18 Fair Fair 34.15349 -
117.87618
331 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 40 20 Fair Fair 34.15348 -
117.87621
332 Juglans californica
Southern
California black
walnut Yes 10 2 10 0 0 0 0 40 30 Fair Fair 34.153492 -117.8762 333 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 30 Fair Poor 34.153478 -
117.87628
334 Juglans californica
Southern
California black
walnut Yes 21 2 21 0 0 0 0 30 30 Fair Poor 34.153435
-
117.87619
335 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 40 20 Fair Fair 34.153433 -117.8762 336 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 20 Fair Fair 34.153447 -
117.87617
337 Corymbia maculata spotted gum Yes 39 2 39 0 0 0 0 50 40 Fair Fair 34.153336 -
117.87625
338 Corymbia maculata spotted gum Yes 44 1 44 0 0 0 0 55 50 Fair Fair 34.153279 -
117.87621
339 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 15 Fair Poor 34.153264 -
117.87612
340 Juglans californica
Southern
California black
walnut Yes 19 3 19 0 0 0 0 25 20 Fair Fair 34.15325
-
117.87598
341 Quercus agrifolia coast live oak Yes 11 2 11 0 0 0 0 20 15 Fair Fair 34.153246 -
117.87596
342 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Fair 34.153193 -
117.87592
343 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Good Poor 34.153172 -117.8759 344 Quercus agrifolia coast live oak Yes 21 2 21 0 0 0 0 30 23 Good Fair 34.153155 -
117.87583
Item #8. Page 810
Meeting Date: 1/24/2023 / Packet Page #: 875
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
345 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 30 15 Poor Poor 34.153128 -
117.87591
347 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Fair Fair 34.153029 -
117.87573
348 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 30 Fair Fair 34.153084 -
117.87578
349 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 15 15 Fair Poor 34.153136 -
117.87571
351 Juglans californica
Southern
California black
walnut Yes 8 1 8 0 0 0 0 30 15 Fair Poor 34.153059
-
117.87549
352 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 25 15 Fair Fair 34.153056 -
117.87568
353 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Fair 34.153023 -
117.87567
355 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Fair Poor 34.153005 -
117.87552
356 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 20 Fair Fair 34.152896 -
117.87549
357 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 20 Fair Fair 34.152856 -
117.87551
358 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 12 9 Good Poor 34.152829 -
117.87547
359 Corymbia maculata spotted gum Yes 31 1 31 0 0 0 0 50 40 Poor Poor 34.152862 -
117.87548
360 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Fair Fair 34.152809 -
117.87549
361 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Fair Fair 34.152868 -
117.87546
362 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 40 20 Fair Fair 34.152858 -
117.87542
363 Juglans californica
Southern
California black
walnut Yes 10 2 5 5 0 0 0 20 10 Poor Poor stem of 3 34.152821 -
117.87532
364 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 10 20 Poor Poor broke in half 34.152818 -117.8753 365 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Fair Fair 34.152811 -
117.87536
366 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Fair Fair 34.152808 -
117.87536
367 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Fair Fair 34.152801 -
117.87537
368 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 15 9 Good Poor 34.152776 -
117.87542
369 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 6 4 Poor Poor stump sprout 34.152767 -
117.87537
Item #8. Page 811
Meeting Date: 1/24/2023 / Packet Page #: 876
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
370 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 25 20 Fair Fair 34.152759 -
117.87536
371 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 20 Fair Fair 34.152754 -
117.87527
372 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Fair 34.152751 -
117.87526
374 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 20 Good Fair 34.15274 -
117.87521
375 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 40 30 Good Fair 34.152721 -
117.87519
376 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 20 Good Fair 34.152732 -
117.87517
377 Juglans californica
Southern
California black
walnut Yes 16 3 6 5 5 0 0 15 15 Fair Poor 34.152737
-
117.87512
378 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 40 25 Good Fair 34.152668 -
117.87516
379 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 15 Good Fair 34.152682 -
117.87523
380 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 20 Good Fair 34.152685 -
117.87526
381 Juglans californica
Southern
California black
walnut Yes 24 4 8 8 4 4 0 15 15 Fair Fair 34.153116
-
117.87534
382 Juglans californica
Southern
California black
walnut Yes 20 4 6 6 4 4 0 15 15 Fair Fair 34.153095
-
117.87539
383 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Good Fair 34.152646 -
117.87525
384 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 14 Good Fair 34.15261 -
117.87525
385 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 40 20 Good Fair 34.152599 -
117.87525
386 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Good Fair 34.152643 -
117.87522
387 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 15 Good Fair 34.152615 -
117.87517
388 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 15 Fair Fair 34.15257 -
117.87517
389 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 40 25 Good Fair 34.152589 -
117.87514
391 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 10 Good Fair 34.152566 -
117.87509
392 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Good Fair 34.152643 -
117.87511
Item #8. Page 812
Meeting Date: 1/24/2023 / Packet Page #: 877
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
393 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 20 Fair Fair 34.152688 -
117.87504
394 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 12 10 Good Poor 34.152689 -
117.87508
395 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 40 20 Fair Fair 34.152622 -
117.87499
396 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Fair Fair 34.152612 -
117.87499
397 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 45 30 Good Fair 34.152598 -
117.87501
398 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 15 Fair Poor 34.15259 -
117.87503
399 Quercus agrifolia coast live oak Yes 17 2 9 8 0 0 0 35 20 Fair Poor 34.15257 -
117.87498
400 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 20 Fair Poor 34.152591 -
117.87493
401 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 20 Fair Fair 34.152574 -
117.87494
402 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 40 30 Good Fair 34.152568 -
117.87495
403 Ceratonia siliqua carob Yes 48 4 16 16 10 6 0 30 20 Good Fair 34.152621 -
117.87489
405 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 15 Fair Poor 34.152595 -
117.87487
406 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 15 Fair Fair 34.152596 -
117.87488
407 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 40 20 Good Fair 34.152548 -
117.87475
408 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 45 20 Good Fair 34.152563 -
117.87476
409 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Good 34.15258 -
117.87477
410 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Poor Poor 34.152615 -
117.87477
411 Quercus agrifolia coast live oak Yes 20 2 20 0 0 0 0 40 15 Fair Poor 34.152655 -
117.87479
412 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 45 15 Fair Poor 34.152672 -
117.87479
414 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 15 Fair Poor 34.152689 -
117.87479
415 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 40 15 Fair Poor 34.152699 -
117.87476
416 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 35 15 Fair Poor 34.152684 -
117.87473
417 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 40 15 Fair Poor 34.152724 -
117.87479
Item #8. Page 813
Meeting Date: 1/24/2023 / Packet Page #: 878
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
418 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Poor 34.152724 -
117.87479
419 Quercus agrifolia coast live oak Yes 21 2 21 0 0 0 0 40 20 Fair Poor 34.152746 -
117.87478
420 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 40 15 Fair Poor 34.152798 -
117.87478
421 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 25 Fair Fair 34.152794 -
117.87481
422 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 35 30 Fair Fair 34.152839 -
117.87475
423 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 30 Fair Fair 34.152844 -
117.87475
424 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 45 30 Good Fair 34.152852 -
117.87474
425 Quercus agrifolia coast live oak Yes 29 3 29 0 0 0 0 45 30 Fair Fair 34.152821 -
117.87469
426 Quercus agrifolia coast live oak Yes 28 4 28 0 0 0 0 40 40 Fair Fair 34.152805 -
117.87471
427 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.152808 -
117.87471
428 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 40 15 Fair Poor 34.152741 -
117.87475
429 Quercus agrifolia coast live oak Yes 18 2 18 0 0 0 0 35 15 Fair Poor 34.152717 -
117.87476
430 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 10 Fair Poor 34.152729 -
117.87478
431 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 15 Fair Poor 34.152718 -
117.87471
432 Quercus agrifolia coast live oak Yes 24 3 24 0 0 0 0 30 15 Fair Poor 34.152701 -
117.87466
433 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.152632 -
117.87467
434 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 15 Fair Poor 34.152627 -
117.87467
435 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 25 Fair Fair 34.152632 -117.8747 436 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 45 30 Good Fair 34.152602 -
117.87469
437 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 20 Good Fair 34.152562 -
117.87472
438
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 70 15 Fair Fair 34.152649
-
117.87459
440
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 65 15 Fair Fair 34.15271
-
117.87459
442
Washingtonia
robusta
Mexican fan
palm Yes 12 1 12 0 0 0 0 55 15 Fair Fair 34.152777 -117.8746 443
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 55 15 Fair Fair 34.152807
-
117.87464
Item #8. Page 814
Meeting Date: 1/24/2023 / Packet Page #: 879
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
444
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 65 15 Fair Fair 34.152913
-
117.87462
445
Washingtonia
robusta
Mexican fan
palm Yes 10 1 10 0 0 0 0 55 15 Fair Fair 34.152939
-
117.87462
446 Platanus racemosa
California
sycamore Yes 10 1 10 0 0 0 0 18 15 Fair Poor stump sprout 34.153132 -
117.87482
447 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 15 Fair Poor stump sprout 34.153127 -
117.87475
448 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 18 Good Poor stump sprout 34.153096 -
117.87472
449 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 18 Good Poor stump sprout 34.153106 -
117.87471
450 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 35 20 Fair Poor stump sprout 34.153248 -
117.87479
451 Quercus agrifolia coast live oak Yes 47 1 47 0 0 0 0 40 40 Fair Fair stump sprout 34.153279 -
117.87487
452 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 20 30 Poor Poor stump sprout 34.153282 -117.8749 453 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 35 18 Poor Poor stump sprout 34.15332 -
117.87487
454 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 20 Fair Poor stump sprout 34.15331 -
117.87483
455 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 40 15 Fair Poor stump sprout 34.153338 -
117.87481
456 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 40 45 Fair Poor stump sprout 34.153371 -
117.87476
458
Washingtonia
robusta
Mexican fan
palm Yes 16 1 16 0 0 0 0 60 15 Good Fair 34.153369
-
117.87451
459 Juglans californica
Southern
California black
walnut Yes 42 3 42 0 0 0 0 25 30 Fair Poor 34.153446
-
117.87466
460 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 45 30 Fair Fair 34.153465 -117.8745 461 Phoenix canariensis
Canary Island
date palm Yes 28 1 28 0 0 0 0 30 20 Fair Fair 34.153342 -
117.87449
462 Phoenix canariensis
Canary Island
date palm Yes 26 1 26 0 0 0 0 10 15 Good Fair 34.153352 -
117.87451
463 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 30 14 Good Good 34.153556 -
117.87449
464 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 30 30 Poor Poor 34.153271 -
117.87445
465 Quercus agrifolia coast live oak Yes 22 2 14 8 0 0 0 40 20 Fair Fair 34.153156 -
117.87445
466 Quercus agrifolia coast live oak Yes 19 2 11 8 0 0 0 30 20 Fair Fair 34.153162 -
117.87446
467 Quercus agrifolia coast live oak Yes 26 2 13 13 0 0 0 40 20 Fair Fair 34.153106 -
117.87443
Item #8. Page 815
Meeting Date: 1/24/2023 / Packet Page #: 880
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
468 Quercus agrifolia coast live oak Yes 32 1 32 0 0 0 0 40 30 Fair Poor 34.153085 -117.8744 470 Quercus agrifolia coast live oak Yes 32 1 32 0 0 0 0 45 35 Fair Fair 34.152917 -
117.87451
471 Juglans californica
Southern
California black
walnut Yes 18 1 18 0 0 0 0 20 30 Fair Poor 34.153134
-
117.87446
475 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 50 20 Fair Fair 34.152891 -
117.87451
476 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 20 Fair Fair 34.152904 -
117.87452
478 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 45 25 Fair Fair 34.152849 -
117.87437
479 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 25 20 Good Good 34.152849 -
117.87438
480 Quercus agrifolia coast live oak Yes 43 7 7 9 9 9 9 30 40 Fair Poor additional stems 7,7 34.152807 -
117.87433
482 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 30 14 Good Fair 34.152765 -
117.87439
483 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 18 Good Fair 34.152753 -
117.87442
484 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 30 14 Good Poor 34.152724 -
117.87435
485 Quercus agrifolia coast live oak Yes 41 4 41 0 0 0 0 40 35 Fair Fair 34.152793 -
117.87445
486 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 20 Good Fair 34.152814 -
117.87441
487 Quercus agrifolia coast live oak Yes 17 3 17 0 0 0 0 50 30 Good Fair 34.152835 -
117.87455
488 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 50 25 Fair Fair 34.152825 -
117.87456
489 Quercus agrifolia coast live oak Yes 27 2 27 0 0 0 0 35 30 Fair Poor 34.152806 -
117.87455
490 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 8 Good Poor 34.152646 -
117.87435
491 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 20 Good Fair 34.152609 -
117.87431
492 Olea europaea fruitless olive Yes 16 4 16 0 0 0 0 20 20 Good Poor 34.152587 -
117.87437
494 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 25 Fair Fair 34.15259 -
117.87446
495
Sambucus
canadensis
American
elderberry Yes 11 2 11 0 0 0 0 15 20 Fair Fair 34.152537 -117.8744 497 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 12 10 Fair Poor 34.152605 -
117.87426
498 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 35 15 Fair Poor 34.152621 -
117.87421
Item #8. Page 816
Meeting Date: 1/24/2023 / Packet Page #: 881
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
499 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 12 Fair Poor 34.152604 -
117.87422
500 Olea europaea fruitless olive Yes 23 2 23 0 0 0 0 20 25 Good Poor 34.152495 -
117.87428
501 Olea europaea fruitless olive Yes 11 1 11 0 0 0 0 40 20 Fair Fair 34.152677 -
117.87414
502 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 25 20 Fair Fair 34.152746 -
117.87416
503 Olea europaea fruitless olive Yes 30 5 30 0 0 0 0 35 30 Good Poor 34.152759 -
117.87424
504 Juglans californica
Southern
California black
walnut Yes 12 2 12 0 0 0 0 15 15 Fair Fair 34.152768
-
117.87418
505 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 35 20 Fair Fair 34.152695 -
117.87409
506 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 20 Fair Fair 34.152627 -
117.87406
507 Olea europaea fruitless olive Yes 12 2 12 0 0 0 0 20 20 Fair Poor 34.152597 -
117.87408
508 Pinus canariensis
Canary Island
pine Yes 28 1 28 0 0 0 0 70 25 Fair Poor 34.152535
-
117.87406
509 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 16 8 Poor Poor stump sprout 34.152564 -
117.87406
510 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 20 Fair Fair 34.152643 -
117.87402
512 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 30 Poor Poor 34.152618 -
117.87391
513 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 30 Fair Good 34.15253 -
117.87398
514 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 15 Good Poor #514_#515 tagged on
same tree 34.152501 -117.8739
516 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 25 15 Good Poor 34.152502 -117.8739 517 Phoenix canariensis
Canary Island
date palm Yes 27 1 27 0 0 0 0 30 20 Fair Good 34.152559 -
117.87392
518 Phoenix canariensis
Canary Island
date palm Yes 27 1 27 0 0 0 0 50 20 Fair Good 34.152582 -
117.87389
519 Phoenix canariensis
Canary Island
date palm Yes 27 1 27 0 0 0 0 45 15 Fair Good 34.152568 -
117.87384
520 Phoenix canariensis
Canary Island
date palm Yes 27 1 27 0 0 0 0 30 15 Fair Fair 34.152561 -
117.87381
521 Phoenix canariensis
Canary Island
date palm Yes 22 1 22 0 0 0 0 45 15 Fair Good 34.152561 -
117.87376
522 Platauna racemosa
California
sycamore Yes 14 1 14 0 0 0 0 25 20 Fair Fair 34.152585
-
117.87366
Item #8. Page 817
Meeting Date: 1/24/2023 / Packet Page #: 882
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
523 Phoenix canariensis
Canary Island
date palm Yes 24 1 24 0 0 0 0 30 15 Good Good 34.152659 -
117.87379
524 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 14 10 Good Poor stump sprout 34.152731 -
117.87362
525 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 15 20 Good Poor stump sprout 34.152731 -
117.87362
526 Quercus agrifolia coast live oak Yes 47 4 47 0 0 0 0 45 35 Fair Poor 34.15278 -
117.87367
527 Eucalyptus robusta
swamp
mahogany Yes 17 1 17 0 0 0 0 25 30 Good Poor 34.152772
-
117.87363
528 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 20 12 Good Poor 34.152831 -117.8737 529 Juglans californica
Southern
California black
walnut Yes 12 1 12 0 0 0 0 25 15 Fair Poor stump sprout 34.152843 -
117.87371
530 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 15 Good Fair 34.152843 -117.8737 531 Phoenix canariensis
Canary Island
date palm Yes 11 1 11 0 0 0 0 30 18 Good Good 34.1529
-
117.87336
532 Phoenix canariensis
Canary Island
date palm Yes 11 1 11 0 0 0 0 30 18 Good Good 34.152818 -
117.87323
534 Quercus agrifolia coast live oak Yes 62 1 62 0 0 0 0 45 45 Poor Fair 34.15298 -
117.87293
535 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 10 Fair Fair 34.152997 -
117.87297
536 Quercus agrifolia coast live oak Yes 26 1 26 0 0 0 0 35 30 Fair Fair 34.153081 -
117.87298
537 Quercus agrifolia coast live oak Yes 21 1 21 0 0 0 0 50 30 Good Fair 34.153094 -
117.87301
538 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 20 Fair Fair 34.153115 -
117.87303
539
Washingtonia
robusta
Mexican fan
palm Yes 11 1 11 0 0 0 0 30 15 Good Good 34.153179
-
117.87295
540
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 55 15 Good Fair 34.153193
-
117.87295
541 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 30 30 Fair Fair 34.153131 -
117.87299
542 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 25 20 Poor Fair 34.153183 -
117.87305
543 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 20 30 Fair Poor 34.153267 -
117.87306
544 Quercus agrifolia coast live oak Yes 46 5 46 0 0 0 0 50 30 Poor Poor 34.153298 -
117.87314
545 Quercus agrifolia coast live oak Yes 26 2 26 0 0 0 0 30 20 Fair Poor 34.153384 -117.8731 547 Quercus agrifolia coast live oak Yes 37 2 37 0 0 0 0 35 30 Fair Poor 34.153459 -
117.87311
Item #8. Page 818
Meeting Date: 1/24/2023 / Packet Page #: 883
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
548 Quercus agrifolia coast live oak Yes 15 2 15 0 0 0 0 25 20 Fair Poor 34.153454 -
117.87316
549 Quercus agrifolia coast live oak Yes 40 2 40 0 0 0 0 40 25 Fair Poor 34.153453 -
117.87316
550 Quercus agrifolia coast live oak Yes 24 2 24 0 0 0 0 30 20 Fair Poor 34.153477 -
117.87315
551 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Fair Poor 34.153504 -
117.87317
552 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 20 15 Fair Poor 34.153504 -
117.87317
553 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 20 Fair Poor 34.1535 -117.8732 554 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 30 20 Fair Poor 34.153506 -117.8732 556 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 25 20 Poor Fair 34.153535 -
117.87323
557 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Fair Fair 34.153587 -
117.87323
558 Quercus agrifolia coast live oak Yes 35 2 35 0 0 0 0 35 25 Fair Fair 34.153554 -
117.87314
560 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 20 15 Poor Poor 34.153596 -
117.87312
561 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 30 20 Poor Poor 34.153692 -
117.87323
562 Quercus agrifolia coast live oak Yes 27 1 27 0 0 0 0 50 30 Fair Fair 34.15375 -
117.87328
563 Platanus racemosa
California
sycamore Yes 11 1 11 0 0 0 0 25 20 Poor Poor 34.153751
-
117.87328
564 Juglans californica
Southern
California black
walnut Yes 8 1 8 0 0 0 0 20 15 Poor Poor
main stem is dead,
stump sprout at base 34.153751
-
117.87325
566 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 45 30 Poor Poor 34.153778 -
117.87314
567 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 30 20 Poor Poor 34.153793 -
117.87315
568 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 15 Poor Poor 34.153808 -
117.87315
569 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 35 15 Fair Poor 34.153816 -
117.87317
570 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 10 6 Fair Poor 34.153878 -
117.87319
571 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 15 Fair Fair 34.153856 -
117.87324
572 Juglans californica
Southern
California black
walnut Yes 11 1 11 0 0 0 0 20 30 Good Poor stump sprout 34.153903 -117.8732 573 Quercus agrifolia coast live oak Yes 31 1 31 0 0 0 0 45 35 Fair Fair 34.153906 -
117.87314
Item #8. Page 819
Meeting Date: 1/24/2023 / Packet Page #: 884
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
574 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 45 30 Fair Fair 34.153917 -
117.87311
575 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 35 Fair Fair 34.15394 -
117.87311
577 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Fair 34.154033 -
117.87313
578 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Good 34.154045 -
117.87313
579 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 25 15 Fair Poor 34.154123 -
117.87313
580 Quercus agrifolia coast live oak Yes 28 4 28 0 0 0 0 25 30 Fair Poor 34.154149 -
117.87312
581 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 15 Fair Poor 34.154167 -
117.87305
583 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 35 30 Poor Poor 34.154061 -
117.87291
584 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 20 Fair Poor 34.154173 -117.873 585 Quercus agrifolia coast live oak Yes 24 1 24 0 0 0 0 45 30 Poor Fair 34.154161 -
117.87295
586 Juglans californica
Southern
California black
walnut Yes 11 2 11 0 0 0 0 15 15 Fair Poor 34.154035
-
117.87289
587 Quercus agrifolia coast live oak Yes 23 1 23 0 0 0 0 40 30 Fair Poor 34.15399 -
117.87288
588 Quercus agrifolia coast live oak Yes 45 2 45 0 0 0 0 40 30 Good Fair 34.153863 -
117.87293
589 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 30 15 Fair Fair 34.15376 -117.873 590 Juglans californica
Southern
California black
walnut Yes 15 2 15 0 0 0 0 20 30 Poor Poor 34.153737 -117.873 591 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 30 Good Fair 34.153674 -
117.87293
592 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 30 20 Fair Poor 34.153566 -
117.87299
593 Juglans californica
Southern
California black
walnut Yes 8 1 8 0 0 0 0 15 20 Good Poor 34.153608
-
117.87297
594 Platanus racemosa
California
sycamore Yes 20 1 20 0 0 0 0 45 30 Fair Poor 34.153522
-
117.87296
595 Quercus agrifolia coast live oak Yes 37 4 37 0 0 0 0 45 40 Fair Fair 34.153203 -117.8728 597 Olea europaea fruitless olive Yes 10 1 10 0 0 0 0 12 12 Good Poor 34.153072 -
117.87279
598 Quercus agrifolia coast live oak Yes 37 2 37 0 0 0 0 45 30 Poor Poor 34.152975 -
117.87271
Item #8. Page 820
Meeting Date: 1/24/2023 / Packet Page #: 885
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
599 Olea europaea fruitless olive Yes 17 2 17 0 0 0 0 15 15 Good Poor stump sprout 34.153003 -
117.87265
600 Olea europaea fruitless olive Yes 13 2 13 0 0 0 0 12 15 Good Poor 34.152969 -
117.87272
601 Quercus agrifolia coast live oak Yes 28 1 28 0 0 0 0 45 15 Poor Poor behind fence on
adjacent property, no
tag 34.150671
-
117.87295
602 Quercus agrifolia coast live oak Yes 17 1 17 0 0 0 0 20 15 Poor Poor behind fence on
adjacent property, no
tag 34.151077
-
117.87318
604 Olea europaea fruitless olive Yes 15 2 8 7 0 0 0 25 20 Fair Fair 34.151806 -
117.87383
608 Juglans regia English walnut Yes 11 2 6 5 0 0 0 20 15 Fair Fair 34.152226 -
117.87496
610 Platanus racemosa
California
sycamore Yes 16 4 4 4 4 4 0 15 15 Fair Poor 34.152358
-
117.87523
612 Platanus racemosa
California
sycamore Yes 18 4 6 4 4 4 0 25 15 Fair Poor 34.152498
-
117.87535
615
Pittosporum
undulatum Victorian box Yes 21 9 5 4 4 4 4 20 15 Fair Poor additional stems of 3, 5,
4, 4 34.152209
-
117.87545
616 Quercus agrifolia coast live oak Yes 42 2 21 21 0 0 0 35 30 Poor Poor 34.15222 -117.8754 617 Quercus agrifolia coast live oak Yes 49 2 25 24 0 0 0 45 30 Poor Poor 34.152215 -
117.87541
618 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 55 40 Poor Fair 34.152191 -
117.87531
619 Quercus agrifolia coast live oak Yes 38 1 38 0 0 0 0 60 50 Fair Fair 34.152187 -
117.87526
620 Quercus agrifolia coast live oak Yes 23 2 12 11 0 0 0 40 30 Fair Fair 34.152177 -
117.87512
621 Schinus molle
Peruvian
pepper Yes 17 1 17 0 0 0 0 18 20 Fair Fair 34.15223
-
117.87568
623 Ficus benjamina weeping fig Yes 63 6 14 12 10 14 13 45 50 Fair Poor additional stem of 7 34.152185 -
117.87578
624 Pinus pinea
Italian stone
pine Yes 25 1 25 0 0 0 0 45 50 Fair Fair 34.152174
-
117.87589
626
Cedrus atlantica
'glauca' blue atlas cedar Yes 16 3 6 5 5 0 0 30 15 Fair Poor 34.152072 -
117.87611
627 Pinus pinea
Italian stone
pine Yes 38 1 38 0 0 0 0 60 40 Fair Poor 34.152047
-
117.87615
629 Citrus spp. citrus tree Yes 12 3 4 4 4 0 0 10 9 Fair Fair 34.152277 -
117.87596
630 Citrus spp. citrus tree Yes 10 4 5 5 0 0 0 10 9 Fair Fair stem of 3 34.152304 -
117.87591
631 Citrus spp. citrus tree Yes 18 3 9 5 4 0 0 10 9 Fair Fair 34.152325 -
117.87585
Item #8. Page 821
Meeting Date: 1/24/2023 / Packet Page #: 886
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
634 Ficus benjamina weeping fig Yes 13 2 7 6 0 0 0 25 15 Good Poor 34.152465 -
117.87587
636
Schinus
terebinthifolia
Brazilian
pepper Yes 14 4 8 6 0 0 0 20 20 Fair Poor stems of 3,3 34.152585 -117.8758 637
Washingtonia
robusta
Mexican fan
palm Yes 17 1 17 0 0 0 0 55 12 Fair Fair 34.152742
-
117.87604
641 Quercus agrifolia coast live oak Yes 15 2 9 6 0 0 0 30 18 Fair Fair 34.15287 -
117.87611
643 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 15 Poor Poor 34.153006 -
117.87618
644
Washingtonia
robusta
Mexican fan
palm Yes 14 1 14 0 0 0 0 65 12 Poor Fair 34.153
-
117.87626
645 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 18 15 Poor Poor 34.152989 -
117.87627
646 Quercus agrifolia coast live oak Yes 18 3 9 5 4 0 0 25 15 Fair Poor 34.152993 -
117.87632
647 Quercus agrifolia coast live oak Yes 19 2 11 8 0 0 0 20 15 Fair Poor 34.152964 -
117.87635
648 Quercus agrifolia coast live oak Yes 14 3 10 4 0 0 0 15 12 Poor Poor stem of 3 34.152932 -
117.87635
649 Quercus agrifolia coast live oak Yes 18 2 10 8 0 0 0 15 10 Poor Poor 34.152903 -
117.87636
650 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 10 Poor Poor 34.152895 -
117.87638
651 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 10 Poor Poor 34.15289 -
117.87637
652 Quercus agrifolia coast live oak Yes 16 2 9 7 0 0 0 25 10 Poor Poor 34.152861 -
117.87641
653 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 12 Fair Poor 34.15282 -
117.87639
654 Quercus agrifolia coast live oak Yes 17 2 9 8 0 0 0 10 8 Poor Poor 34.15288 -
117.87646
655 Quercus agrifolia coast live oak Yes 24 2 14 10 0 0 0 25 10 Fair Poor 34.15288 -
117.87646
656 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 10 8 Fair Poor broke trunk 34.152884 -
117.87649
657 Quercus agrifolia coast live oak Yes 32 4 12 7 7 6 0 18 15 Fair Poor 34.152923 -
117.87655
659 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 25 10 Poor Poor 34.153133 -
117.87663
660 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 12 8 Poor Poor 34.153153 -
117.87661
661 Quercus agrifolia coast live oak Yes 18 2 10 8 0 0 0 25 10 Poor Poor 34.153155 -
117.87663
662 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 10 10 Poor Poor 34.153157 -
117.87669
Item #8. Page 822
Meeting Date: 1/24/2023 / Packet Page #: 887
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
666 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 18 Fair Fair Steep, no access
estimated dbh 34.153892
-
117.87643
667 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 18 Fair Fair Steep, no access
estimated dbh 34.153869
-
117.87637
669 Quercus agrifolia coast live oak Yes 14 0 6 8 0 0 0 20 15 Poor Poor 34.15317 -
117.87643
670 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 15 Poor Poor 34.153134 -
117.87642
671 Olea europaea fruitless olive Yes 56 5 21 13 9 6 7 20 10 Poor Poor 34.153085 -
117.87643
672 Quercus agrifolia coast live oak Yes 13 2 8 5 0 0 0 20 8 Fair Poor 34.153078 -
117.87641
673 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.153078 -
117.87639
674 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 15 8 Fair Poor 34.153106 -
117.87636
675 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 25 20 Poor Poor 34.153074 -117.8763 676 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 30 15 Poor Poor 34.153044 -117.8763 677 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 30 15 Poor Fair 34.15318 -
117.87632
678 Quercus agrifolia coast live oak Yes 24 1 7 11 6 0 0 30 20 Fair Poor 34.153211 -117.8763 679 Quercus agrifolia coast live oak Yes 24 1 7 11 6 0 0 30 20 Fair Poor 34.153362 -117.8763 679 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 15 Poor Poor Steep, no tag, estimate
dbh 34.153447
-
117.87649
680 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 35 Fair Fair Steep, no tag, estimate
dbh 34.153456
-
117.87644
681 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 45 35 Fair Fair Steep, no tag, estimate
dbh 34.153454 -117.8764
682 Quercus agrifolia coast live oak Yes 22 2 16 6 0 0 0 50 30 Fair Fair Steep, no tag, estimate
dbh 34.153477
-
117.87641
683 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair Steep, no tag, estimate
dbh 34.153519
-
117.87643
684 Quercus agrifolia coast live oak Yes 28 2 14 14 0 0 0 25 30 Poor Fair Steep, no tag, estimate
dbh 34.153525 -117.8764
685 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 15 15 Fair Poor 34.153704 -117.8763 686 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 30 15 Fair Fair 34.153658 -
117.87623
687 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 10 10 Fair Poor sprout off fallen tree no
tag access 34.153714
-
117.87614
688 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 17 12 Fair Fair Steep, no tag, estimate
dbh 34.153846
-
117.87631
689 Quercus agrifolia coast live oak Yes 18 1 18 0 0 0 0 10 18 Fair Poor 34.153828 -
117.87629
690 Quercus agrifolia coast live oak Yes 12 1 7 5 0 0 0 15 18 Fair Poor 34.153842 -
117.87624
Item #8. Page 823
Meeting Date: 1/24/2023 / Packet Page #: 888
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
691 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 15 6 Poor Poor Steep, no tag, estimate
dbh 34.153742
-
117.87613
692 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 25 15 Good Fair Steep, no tag, estimate
dbh 34.153768
-
117.87611
693 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 10 Fair Fair 34.153822 -117.8761 695 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 23 18 Fair Poor 34.153852 -
117.87621
696 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.15388 -
117.87615
697 Platanus racemosa
California
sycamore Yes 20 1 20 0 0 0 0 45 20 Poor Poor 34.15393
-
117.87618
699 Juglans californica
Southern
California black
walnut Yes 8 1 8 0 0 0 0 20 18 Good Fair
Steep, no access
estimated dbh 34.154082
-
117.87627
700 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 18 Fair Poor 34.15399 -
117.87617
701 Juglans californica
Southern
California black
walnut Yes 9 1 9 0 0 0 0 20 15 Fair Poor no tag, couldn't access 34.154056 -
117.87612
702 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 15 Fair Fair 34.154095 -
117.87614
703 Quercus agrifolia coast live oak Yes 26 2 13 13 0 0 0 30 30 Fair Poor 34.154158 -
117.87615
704 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 45 20 Fair Poor no tag, couldn't access 34.15416 -
117.87615
711 Juglans californica
Southern
California black
walnut Yes 24 3 9 7 8 0 0 25 20 Poor Poor no tag, couldn't access 34.153412 -
117.87599
712 Juglans californica
Southern
California black
walnut Yes 16 2 9 7 0 0 0 25 15 Poor Poor no tag, couldn't access 34.153514 -
117.87605
719 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 25 20 Fair Fair 34.150829 -
117.87262
720 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 25 20 Fair Fair 34.150796 -
117.87263
721 Quercus agrifolia coast live oak Yes 12 5 4 4 4 0 0 20 10 Fair Fair stems of 3,3 34.150927 -
117.87263
722 Grevillea robusta silk oak Yes 10 2 5 5 0 0 0 30 23 Fair Fair 34.151096 -
117.87263
723 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 20 Fair Fair 34.151289 -
117.87265
724 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 25 10 Poor Fair 34.151299 -
117.87265
725 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 25 10 Poor Fair 34.151296 -
117.87264
Item #8. Page 824
Meeting Date: 1/24/2023 / Packet Page #: 889
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
726 Quercus agrifolia coast live oak Yes 11 2 7 4 0 0 0 20 10 Poor Poor 34.15131 -
117.87265
728 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 25 15 Fair Fair 34.15135 -
117.87264
730 Quercus agrifolia coast live oak Yes 14 2 7 7 0 0 0 18 22 Fair Fair 34.151395 -
117.87265
732 Quercus agrifolia coast live oak Yes 11 1 11 0 0 0 0 35 15 Poor Fair 34.151452 -
117.87266
734 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 35 15 Fair Fair 34.151476 -
117.87268
735 Quercus agrifolia coast live oak Yes 12 1 12 0 0 0 0 20 10 Fair Fair 34.151501 -
117.87267
736 Schinus molle
Peruvian
pepper Yes 27 5 8 9 6 4 0 15 15 Fair Poor stem of 3 34.15201 -
117.87305
737 Ficus elastica rubber tree Yes 34 1 34 0 0 0 0 25 25 Good Fair 34.152164 -
117.87345
740 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 15 Fair Poor 34.152426 -
117.87381
745 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 30 10 Fair Poor 34.152762 -
117.87474
747 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 15 7 Poor Poor 34.152775 -
117.87472
749 Platanus racemosa
California
sycamore Yes 12 2 6 6 0 0 0 30 15 Fair Fair no tag, couldn't access 34.153071 -117.8747 750 Juglans californica
Southern
California black
walnut Yes 8 2 4 4 0 0 0 20 18 Fair Fair no tag, couldn't access 34.15296 -
117.87472
751 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 15 10 Fair Fair 34.153116 -
117.87467
752 Juglans californica
Southern
California black
walnut Yes 9 1 9 0 0 0 0 12 15 Fair Poor stump sprout 34.153204 -
117.87485
753 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 13 9 Fair Poor 34.153357 -
117.87503
754 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 20 12 Fair Fair 34.153384 -
117.87513
756 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 20 12 Fair Fair no tag, couldn't access 34.153611 -
117.87485
758 Juglans californica
Southern
California black
walnut Yes 18 3 6 6 6 0 0 30 15 Fair Fair
Steep, no tag, estimated
dbh 34.153759
-
117.87461
763 Quercus agrifolia coast live oak Yes 14 1 14 0 0 0 0 30 15 Fair Fair Steep, no tag, estimated
dbh 34.153962
-
117.87461
767 Quercus agrifolia coast live oak Yes 15 1 15 0 0 0 0 30 15 Fair Poor 34.153522 -117.8747 Item #8. Page 825
Meeting Date: 1/24/2023 / Packet Page #: 890
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
769 Platanus racemosa
California
sycamore Yes 15 2 10 5 0 0 0 30 10 Poor Poor 34.153538 -117.8745 771 Juglans californica
Southern
California black
walnut Yes 16 4 4 4 4 4 0 20 40 Good Poor Stump regrowth 34.153129 -
117.87452
772 Quercus agrifolia coast live oak Yes 32 3 11 11 10 0 0 30 20 Fair Poor no tag, couldn't access 34.153024 -
117.87434
773 Juglans californica
Southern
California black
walnut Yes 9 1 9 0 0 0 0 30 20 Good Poor no tag, couldn't access 34.153103 -
117.87445
778 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 45 30 Fair Fair no tag, couldn't access 34.152935 -117.8739 781 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 10 Fair Fair 34.152839 -
117.87311
782 Eucalyptus robusta
swamp
mahogany Yes 26 5 6 5 5 4 6 25 25 Fair Poor stump sprout 34.152832 -
117.87311
793 Quercus agrifolia coast live oak Yes 22 1 22 0 0 0 0 35 15 Fair Fair 34.154194 -117.8732 795 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 12 10 Poor Poor 34.153876 -117.8731 796 Quercus agrifolia coast live oak Yes 10 0 10 0 0 0 0 45 18 Fair Fair no tag, couldn't access 34.153769 -
117.87256
797 Juglans californica
Southern
California black
walnut Yes 10 0 10 0 0 0 0 30 30 Fair Fair no tag, couldn't access 34.15352 -
117.87254
798 Quercus agrifolia coast live oak Yes 16 1 16 0 0 0 0 35 15 Poor Poor 34.153254 -
117.87267
802 Quercus agrifolia coast live oak Yes 8 2 4 4 0 0 0 8 1 Poor Poor 34.152602 -
117.87257
803 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 25 8 Fair Poor located on adjacent
property, did not tag 34.152516
-
117.87255
804 Quercus agrifolia coast live oak Yes 25 1 25 0 0 0 0 35 15 Fair Fair located on adjacent
property, did not tag 34.152507
-
117.87255
805 Quercus agrifolia coast live oak Yes 44 2 28 16 0 0 0 40 20 Fair Fair located on adjacent
property, did not tag 34.152507
-
117.87255
806 Quercus agrifolia coast live oak Yes 20 1 20 0 0 0 0 40 25 Fair Fair located on adjacent
property, did not tag 34.152425
-
117.87258
807 Quercus agrifolia coast live oak Yes 8 1 8 0 0 0 0 20 10 Fair Fair 34.152273 -117.8726 809 Quercus agrifolia coast live oak Yes 10 1 10 0 0 0 0 15 10 Fair Poor 34.152241 -117.8726 810 Quercus agrifolia coast live oak Yes 13 1 13 0 0 0 0 18 15 Fair Fair 34.152154 -
117.87263
811 Quercus agrifolia coast live oak Yes 10 2 5 5 0 0 0 20 15 Poor Fair 34.152052 -
117.87266
812 Quercus agrifolia coast live oak Yes 10 2 5 5 0 0 0 12 10 Fair Poor 34.152002 -
117.87267
813 Schinus molle
Peruvian
pepper Yes 24 5 10 9 5 0 0 20 20 Fair Fair stems of 3,3 34.152037 -
117.87259
Item #8. Page 826
Meeting Date: 1/24/2023 / Packet Page #: 891
Grand Estates Tree Information Matrix (August 2020)
Tree
No. Botanical Name Common Name Protected
Diameter at
Standard
Height
(inches) Stems Stem 1
Stem
2 Stem
3 Stem
4 Stem
5 Height
(Feet)
Width
(Feet) Health Structure Notes Lat. Long.
814 Schinus molle
Peruvian
pepper Yes 33 5 10 8 6 5 4 20 20 Fair Fair 34.152086
-
117.87256
815 Quercus agrifolia coast live oak Yes 18 2 9 9 0 0 0 15 10 Poor Poor 34.152089 -
117.87257
817 Schinus molle
Peruvian
pepper Yes 16 2 8 8 0 0 0 15 20 Fair Poor 34.152142
-
117.87258
818 Schinus molle
Peruvian
pepper Yes 16 2 8 8 0 0 0 15 20 Fair Poor 34.151958
-
117.87268
819 Quercus agrifolia coast live oak Yes 19 1 19 0 0 0 0 25 30 Fair Fair 34.15186 -
117.87262
820 Quercus agrifolia coast live oak Yes 8 4 4 4 0 0 0 25 15 Fair Poor stems of 3,3 34.15189 -
117.87261
821 Schinus molle
Peruvian
pepper Yes 35 3 12 12 11 0 0 25 10 Fair Poor 34.15185
-
117.87258
822 Schinus molle
Peruvian
pepper Yes 34 2 12 12 10 0 0 30 15 Poor Poor 34.151734
-
117.87265
823 Quercus agrifolia coast live oak Yes 21 5 6 5 5 5 0 25 15 Fair Poor stem of 3 34.151735 -
117.87263
824 Quercus agrifolia coast live oak Yes 21 3 8 6 7 0 0 35 15 Fair Poor 34.151751 -
117.87256
826 Quercus agrifolia coast live oak Yes 13 5 5 4 4 0 0 25 15 Fair Poor stems of 2,2 34.151739 -
117.87256
827 Quercus agrifolia coast live oak Yes 19 5 6 5 4 4 0 20 15 Fair Poor stem of 3 34.15171 -
117.87256
828 Olea europaea fruitless olive Yes 36 5 14 9 8 5 0 30 20 Fair Poor stem of 3 34.152233 -
117.87308
829 Eucalyptus cladocalx sugar gum Yes 14 3 6 4 4 0 0 40 12 Fair Poor 34.152504 -
117.87312
830 Eucalyptus cladocalx sugar gum Yes 16 5 3 4 5 4 0 40 12 Fair Poor stem of 3 34.152511 -
117.87314
831 Eucalyptus cladocalx sugar gum Yes 11 2 6 5 0 0 0 40 18 Fair Poor 34.152533 -
117.87315
832 Eucalyptus cladocalx sugar gum Yes 20 4 6 5 5 4 0 40 25 Fair Poor 34.152555 -
117.87312
833 Quercus agrifolia coast live oak Yes 9 1 9 0 0 0 0 35 15 Fair Poor 34.152698 -
117.87282
835 Olea europaea fruitless olive Yes 15 2 8 7 0 0 0 30 20 Fair Poor 34.152793 -
117.87279
708a Platanus racemosa
California
sycamore Yes 11 1 11 0 0 0 0 30 10 Poor Poor 34.154152
-
117.87616
708b Juglans californica
Southern
California black
walnut Yes 9 4 5 4 0 0 0 10 10 Fair Poor
no tag, couldn't access,
stems of 3,2 34.153741
-
117.87595
Item #8. Page 827
Meeting Date: 1/24/2023 / Packet Page #: 892
Appendix B-2
Draft Architectural Landscape Plans and Tree Removals
Item #8. Page 828
Meeting Date: 1/24/2023 / Packet Page #: 893
Item #8. Page 829
Meeting Date: 1/24/2023 / Packet Page #: 894
GRAND AVENUE PALM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STRE T "A" STREET PL PL PL PL PL PL PLPL PL PL PL PL PLPL PLPL PL PLPL PL PL PL PL PL PL PL PL PL PL PLPL PLPL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PLPL PL LOT 1(E) POOL HOUSE (E) RESIDENCE (E) GAZEBO (E) GUEST HOUSE LOT 3 ASPHALT PAVED RD. ASPHALT PAVED RD. ASPHALT PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 2 SHEET INDEX EXISTING TREES DATA (REMAIN) EXISTING TREES DATA (REMAIN) CONCEPTUAL LANDSCAPE PLAN L-1 TITLE PLAN R.S. R.S. CHECKED 02-21-2022 DATE DRAWN 21015 JOB NO. SHEET OF 13 SHEETS REVISIONS BY p L R i STERi l E h D GE PI T DATE RENEWAL DATE 1 3 PE NDSC S . Ma A y A SIGNATURE 0 A HC I R CE 4 T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA CITY COMMENTS 09-01-2021 1 CITY COMMENTS 02-07-2022 2 0 NORTH 25' 50' 100' L-2.1 L-2.2 Phil May Landscape Architecture 2532 Wallace Ave. Fullerton, CA 92831 909-373-1959 LANDSCAPE ARCHITECT CONSULTANTS DREAMLAND INVESTMENT INVESTMENT LLC 626.236.7388 OWNER / DEVELOPER GIRON ENGINEERS INC. 654 S. GLENDORA AVE. 626.335.8782 CIVIL ENGINEER L-4 L-5 L-6 L-7 CERTIFICATION OF LANDSCAPE DESIGN I hereby certify that: (1) I am a professional appropriately licensed in the State of California to provide professional landscape design services. (2) The landscape design and water use calculations for the property located at (3) (provide street address or parcel number(s)) were prepared by me or under my supervision. (4) The landscape design and water use calculations for the identified property comply with the requirements of the City of Glendora Water Efficient Landscape Ordinance (Municipal Code Chapter 13.18) and the City of Glendora Water Efficient Landscape Guidelines. (5) The information I have provided in this Certificate of Landscape Design is true and correct and is hereby submitted in compliance with the City of Glendora Water Efficient Landscape Guidelines. Print Name Date Signature License Number Address Telephone E-mail Address Landscape Design Professional's Stamp p L R i STERi l E h D GE PI T DATE 05-31-23 RENEWAL DATE 13 PE NDSC . a S M A y ASIGNATURE 0 A HC I R CE 4T L-2 TREE INVENTORY PLAN (REMAIN) L-8 Month Adjust Irrigation Schedule Inspect Tree Staking Flush Drip Valves Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec RECOMMENDED MINIMUM LANDSCAPE MAINTENANCE SCHEDULE WEEKLY TASKS HOA LANDSCAPE AREAS MINIMUM RECOMMENDED YEARLY MAINTENANCE SCHEDULE Check all irrigation equipment and adjust/ align as required. Repair irrigation equipment with originally specified materials as needed. Inspect all landscape areas for pests/ pathogens. Weed all shrub/ groundcover areas as needed. Remove landscape debris. Aerating and dethatching turf areas. Repair planting well and/ or grade around plants to eliminate runoff. Perform corrective pruning to eliminate hazards and damage to plant after 2nd Year of Growth. Add Mulch (Maintain 3" Layer) Fertilization: Reference to Agronomical Soil's report on these plans ARCHITECTURAL LANDSCAPE PLANS THE GRAND ESTATES 950 SILENT RANCH RD., GLENDORA, CA TENTATIVE TRACT MAP NO. 72413 FOOTHILL BLVD ROUTE 66 SIERRA MADRE AVE 210 FWY PALM DR GRAND AVE CITRUS AVE L-3.3 TREE INVENTORY LOT -1 02-21-2021 EXISTING TREES DATA (REMOVE) L-3.1 EXISTING TREES DATA (REMOVE) L-3.2 L-3 TREE INVENTORY PLAN (REMOVE) CONCEPTUAL LANDSCAPE PLAN CONCEPTUAL LANDSCAPE PLAN CONCEPTUAL LANDSCAPE PLAN CONCEPTUAL LANDSCAPE PLAN Item #8. Page 830 Meeting Date: 1/24/2023 / Packet Page #: 895 Item #8. Page 831
Meeting Date: 1/24/2023 / Packet Page #: 896
NUE PALM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STREET (E) POOL HOUSE (E) RESIDENCE (E) GAZEBO (E) GUEST HOUSE LOT 3 ASPHALT PAVED RD. ASPHALT PAVED RD. ASPHALT PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 R.S. R.S. 02-21-2022 21015 OF 13 SHEETS REVISIONS BY p L i STE E h D GE I 1 E NDSC . Ma A y A 0 A HC I R E 4 T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA 12 0 NORTH 25' 50' 100'

TREE INVENTORY PLAN
(TO REMAIN IN PLACE) PRESERVATION NOTES FOR EXISTING TREES TO REMAIN 1. Temporary, protective fending shall be installed around any existing tree that is to be preserved on a project site. This fencing must 5' high, vinyl material and orange color. This fencing shall be placed at a minimum distance of fifteen (15) feet from the trunk of the tree or five (5) feet outside the drip line of the tree, whichever distance is greater. No activity, or material storage shall take place within this fenced-in area. If area must be accessed, the ground must be mitigated with mulch and plywood to absorb the effects of compaction. Signage shall be added to the fencing at spaced intervals to advise that trees are being protected and to keep out. 2. No supplemental irrigation should be introduced to tree base. 3. Limit the percentage of soil compaction within the drip line of tree. 4. No fill in or construction material shall be placed within the drip line of tree. 5. Arborist must be present during excavation near tree to verify minimal damage to root system. 6. Keep proposed drainage flow away from tree protected zone. 2 2 Item #8. Page 832 Meeting Date: 1/24/2023 / Packet Page #: 897
Item #8. Page 833
Meeting Date: 1/24/2023 / Packet Page #: 898
R.S. R.S. 02-21-2022 21015 OF 13 SHEETS REVISIONS BY p L i STERi E h D GE I 1 3 E NDSC . Ma A y A 0 A HC I R E 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA 12

EXISTING TREE

INVENTORY DATA
(TO REMAIN IN PLACE) NOTE: SEE TREE INVENTORY PLAN, SHEET-L2 FOR REFERENCE PRESERVATION NOTES FOR EXISTING TREES TO REMAIN 1. Temporary, protective fending shall be installed around any existing tree that is to be preserved on a project site. This fencing must 5' high, vinyl material and orange color. This fencing shall be placed at a minimum distance of fifteen (15) feet from the trunk of the tree or five (5) feet outside the drip line of the tree, whichever distance is greater. No activity, or material storage shall take place within this fenced-in area. If area must be accessed, the ground must be mitigated with mulch and plywood to absorb the effects of compaction. Signage shall be added to the fencing at spaced intervals to advise that trees are being protected and to keep out. 2. No supplemental irrigation should be introduced to tree base. 3. Limit the percentage of soil compaction within the drip line of tree. 4. No fill in or construction material shall be placed within the drip line of tree. 5. Arborist must be present during excavation near tree to verify minimal damage to root system. 6. Keep proposed drainage flow away from tree protected zone. 2 Item #8. Page 834 Meeting Date: 1/24/2023 / Packet Page #: 899
R.S. R.S. 02-21-2022 21015 OF 13 SHEETS REVISIONS BY p L i STERi E h D GE I 1 3 E NDSC . Ma A y A 0 A HC I R E 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA 12

EXISTING TREE

INVENTORY DATA
(TO REMAIN IN PLACE) NOTE: SEE TREE INVENTORY PLAN, SHEET-L2 FOR REFERENCE PRESERVATION NOTES FOR EXISTING TREES TO REMAIN 1. Temporary, protective fending shall be installed around any existing tree that is to be preserved on a project site. This fencing must 5' high, vinyl material and orange color. This fencing shall be placed at a minimum distance of fifteen (15) feet from the trunk of the tree or five (5) feet outside the drip line of the tree, whichever distance is greater. No activity, or material storage shall take place within this fenced-in area. If area must be accessed, the ground must be mitigated with mulch and plywood to absorb the effects of compaction. Signage shall be added to the fencing at spaced intervals to advise that trees are being protected and to keep out. 2. No supplemental irrigation should be introduced to tree base. 3. Limit the percentage of soil compaction within the drip line of tree. 4. No fill in or construction material shall be placed within the drip line of tree. 5. Arborist must be present during excavation near tree to verify minimal damage to root system. 6. Keep proposed drainage flow away from tree protected zone. 2 Item #8. Page 835 Meeting Date: 1/24/2023 / Packet Page #: 900
NUE PALM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STREET (E) POOL HOUSE (E) RESIDENCE (E) GAZEBO (E) GUEST HOUSE LOT 3 ASPHALT PAVED RD. ASPHALT PAVED RD. ASPHALT PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 R.S. R.S. 02-21-2022 21015 OF 13 SHEETS REVISIONS BY p L i STE E h D GE I 1 E NDSC . Ma A y A 0 A HC I R E 4 T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA 12 0 NORTH 25' 50' 100'

TREE INVENTORY PLAN
(TO BE REMOVE) 1 Item #8. Page 836
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THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA 1
2 EXISTING TREE

INVENTORY DATA
(TO BE REMOVE)
Item #8. Page 838
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APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA 1
2 EXISTING TREE

INVENTORY DATA
(TO BE REMOVE)
Item #8. Page 839
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PL PL PL PL 1 2 3 5 7 8 4 6 36 9 10 11 13 14 15 12 16 19 20 18 17 21 2223 24 25 27 26 31 30 28 29 33 34 35 32 39 38 37 40 41 42 46 43 44 45 49 52 53 51 50 54 55 56 47 48 LOT 1(E) POOL HOUSE (E) RESIDENCE D A VENUEPA LM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STRE T "A" STREET PL PL PL PL PL PL PLPL PL PL PL PL PL PL PLPL PL PLPL PL PL PL PL PL PL PL PL PL PL PLPL PLPL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PLPL PL LOT 1( E) PO OL HO USE (E) RESIDENCE (E ) G A Z E B O (E) GUEST HOUSE LOT 3 ASPHAL T PAVED RD. ASPHAL T PAVED RD. ASPHAL T PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 R.S. R.S. 02-21-2022 21015 OF 13 SHEETS REVISIONS BY p L i STERi E h D E I 1 PE NDSC . Ma A y A 0HC I R E 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA 12 NORTH
TREE INVENTORY LOT -1 L-3.3 KEY MAP 0 8' 16' 32' SCALE: 1/16" = 1'-0" Item #8. Page 840 Meeting Date: 1/24/2023 / Packet Page #: 905 Item #8. Page 841
Meeting Date: 1/24/2023 / Packet Page #: 906
2 2 D A VENUEPA LM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STRE T "A" STREET LOT 3 ASPHAL T PAVED RD. ASPHAL T PAVED RD. ASPHAL T PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 @ SLOPE AREAS HYDRO-SEED MIX 2 R.S. R.S. CHECKED 02-21-2022 DATE DRAWN 21015 JOB NO. SHEET OF 13 SHEETS REVISIONS BY p L R i STERi l E h D GE PI T DATE RENEWAL DATE 1 3 PE NDSC . a S M A y ASIGNATURE 0 A HC I R CE 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA CITY COMMENTS 09-01-2021 1 CITY COMMENTS 02-07-2022 2 NORTH

CONCEPTUAL
LANDSCAPE PLAN 0 10' 20' 40' SCALE: 1" = 20'-0" KEY MAP MATCH LINE, SEE SHEET L-6 MATCH LINE, SEE SHEET L-5 IRRIGATION NOTES 1. All proposed planting of HOA areas to be irrigated with a permanent irrigation system to comply with City of Glendora Water Efficient Landscape and Irrigation Ordinance. 2. All proposed planting outside Fuel Modification Zones, are to be irrigated with a temporarily irrigation system for hydro-seed establishment. 3. North area will be irrigated with a temporarily spray irrigation system for until plant material is established EXISTING TREES TO REMAIN IN PLACE, SEE "EXISTING TREES DATA" SHEETS L-3 & L-4 FOR TREE INFORMATION. 1 Item #8. Page 842 Meeting Date: 1/24/2023 / Packet Page #: 907
Item #8. Page 843
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D A VENUEPA LM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STRE T "A" STREET LOT 3 ASPHAL T PAVED RD. ASPHAL T PAVED RD. ASPHAL T PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 ASPHALT PAVED RD. 2 2 2 2 2 2 @ SLOPE AREAS HYDRO-SEED MIX R.S. R.S. CHECKED 02-21-2022 DATE DRAWN 21015 JOB NO. SHEET OF 13 SHEETS REVISIONS BY p L R i STERi l E h D GE PI T DATE RENEWAL DATE 1 3 PE NDSC . a S M A y ASIGNATURE 0 A HC I R CE 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA CITY COMMENTS 09-01-2021 1 CITY COMMENTS 02-07-2022 2 NORTH 0 10' 20' 40' SCALE: 1" = 20'-0" KEY MAP MATCH LINE, SEE SHEET L-7 MATCH LINE, SEE SHEET L-4 EXISTING TREES TO REMAIN IN PLACE, SEE "EXISTING TREES DATA" SHEETS L-3 & L-4 FOR TREE INFORMATION. IRRIGATION NOTES 1. All proposed planting of HOA areas to be irrigated with a permanent irrigation system to comply with City of Glendora Water Efficient Landscape and Irrigation Ordinance. 2. All proposed planting outside Fuel Modification Zones, are to be irrigated with a temporarily irrigation system for hydro-seed establishment. 3. North area will be irrigated with a temporarily spray irrigation system for until plant material is established

CONCEPTUAL
LANDSCAPE PLAN 1 1 Item #8. Page 844
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LOT 2 LOT 4 PL PL PL PL PL PL PL PL PL PL PL PL PLPL PL (E) POOL HOUSE (E) GUEST HOUSE LOT 3 ASPHALT PAVED RD. 2 2 2 D A VENUEPA LM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STRE T "A" STREET LOT 3 ASPHAL T PAVED RD. ASPHAL T PAVED RD. ASPHAL T PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 2 @ SLOPE AREAS HYDRO-SEED MIX R.S. R.S. CHECKED 02-21-2022 DATE DRAWN 21015 JOB NO. SHEET OF 13 SHEETS REVISIONS BY p L R i STERi l E h D GE PI T DATE RENEWAL DATE 1 3 PE NDSC . a S M A y ASIGNATURE 0 A HC I R CE 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA CITY COMMENTS 09-01-2021 1 CITY COMMENTS 02-07-2022 2 NORTH 0 10' 20' 40' SCALE: 1" = 20'-0" KEY MAP MATCH LINE, SEE SHEET L-4 MATCH LINE, SEE SHEET L-7 EXISTING TREES TO REMAIN IN PLACE, SEE "EXISTING TREES DATA" SHEETS L-3 & L-4 FOR TREE INFORMATION. IRRIGATION NOTES 1. All proposed planting of HOA areas to be irrigated with a permanent irrigation system to comply with City of Glendora Water Efficient Landscape and Irrigation Ordinance. 2. All proposed planting outside Fuel Modification Zones, are to be irrigated with a temporarily irrigation system for hydro-seed establishment. 3. North area will be irrigated with a temporarily spray irrigation system for until plant material is established

CONCEPTUAL
LANDSCAPE PLAN 1 1 Item #8. Page 846
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D A VENUEPA LM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STRE T "A" STREET LOT 3 ASPHAL T PAVED RD. ASPHAL T PAVED RD. ASPHAL T PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 "A" STRE T PL PLPL PL PL PL PL PLPL PL PLPL PLPL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL ASPHALT PAVED RD. 2 2 @ SLOPE AREAS HYDRO-SEED MIX R.S. R.S. CHECKED 02-21-2022 DATE DRAWN 21015 JOB NO. SHEET OF 13 SHEETS REVISIONS BY p L R i STERi l E h D GE PI T DATE RENEWAL DATE 1 3 PE NDSC . a S M A y ASIGNATURE 0 A HC I R CE 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA CITY COMMENTS 09-01-2021 1 CITY COMMENTS 02-07-2022 2 NORTH 0 10' 20' 40' SCALE: 1" = 20'-0" KEY MAP MATCH LINE, SEE SHEET L-8 MATCH LINE, SEE SHEET L-5 MATCH LINE, SEE SHEET L-6 IRRIGATION NOTES 1. All proposed planting of HOA areas to be irrigated with a permanent irrigation system to comply with City of Glendora Water Efficient Landscape and Irrigation Ordinance. 2. All proposed planting outside Fuel Modification Zones, are to be irrigated with a temporarily irrigation system for hydro-seed establishment. 3. North area will be irrigated with a temporarily spray irrigation system for until plant material is established

CONCEPTUAL
LANDSCAPE PLAN 1 1 Item #8. Page 848
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2 GRAND AVENUE PALM DRIVELOT 12 LOT 13 LOT 14 "A" STREET PL PL PL PL PL PL PLPL PL PL PL PL PLPL PLPL PL PL PL D A VENUEPA LM DRIVE LOT 2 LOT 5 LOT 6 LOT 7 LOT 8 LOT 9 LOT 10 LOT 11 LOT 12 LOT 13 LOT 14 LOT 4 "A" STRE T "A" STREET PL PL PL PL PL PL PLPL PL PL PL PL PL PL PLPL PL PLPL PL PL PL PL PL PL PL PL PL PL PLPL PLPL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PL PLPL PL LOT 1( E) PO OL HO USE (E) RESIDENCE (E ) G A Z E B O (E) GUEST HOUSE LOT 3 ASPHAL T PAVED RD. ASPHAL T PAVED RD. ASPHAL T PAVED RD. 2 2 2 2 2 2 2 2 2 2 2 R.S. R.S. CHECKED 02-21-2022 DATE DRAWN 21015 JOB NO. SHEET OF 13 SHEETS REVISIONS BY p L R i STERi l E h D GE PI T DATE RENEWAL DATE 1 3 PE NDSC . a S M A y ASIGNATURE 0 A HC I R CE 4T 05-31-23 02-21-2022 APN: 8684045004

THE GRAND ESTATES
950 SILENT RANCH RD.

GLENDORA, CA CITY COMMENTS 09-01-2021 1 CITY COMMENTS 02-07-2022 2 NORTH 0 10' 20' 40' SCALE: 1" = 20'-0" KEY MAP SECTION VIEW N.T.S GROUNDCOVER PLANTING DETAIL 3 SECTION VIEW N.T.S SHRUB PLANTING DETAIL 2SECTION VIEW N.T.S TREE PLANTING DETAIL 1 MATCH LINE, SEE SHEET L-7 IRRIGATION NOTES 1. All proposed planting of HOA areas to be irrigated with a permanent irrigation system to comply with City of Glendora Water Efficient Landscape and Irrigation Ordinance. 2. All proposed planting outside Fuel Modification Zones, are to be irrigated with a temporarily irrigation system for hydro-seed establishment. 3. North area will be irrigated with a temporarily spray irrigation system for until plant material is established

CONCEPTUAL
LANDSCAPE PLAN 1 Item #8. Page 850
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Appendix C
Cultural Resources Technical Report
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DRAFT

HISTORICAL RESOURCES TECHNICAL REPORT FOR

GRAND ESTATES PROJECT
Prepared for:

City of Glendora
Planning Department
116 East Foothill Boulevard
Glendora, California 91741
Prepared by:

Kate Kaiser, MSHP, Kathryn Haley, MA, and Samantha Murray, MA

38 North Marengo Ave
Pasadena, California 91101
AUGUST 2019
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Printed on 30% post-consumer recycled material.

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Table of Contents
SECTION PAGE NO.

EXECUTIVE SUMMARY ................................................................................................................................................... V 1 INTRODUCTION ................................................................................................................................................. 1

1.1 Project Description and Location ..........................................................................................................1

1.2 Area of Potential Effects (APE)...............................................................................................................1

1.3 Project Personnel ...................................................................................................................................7

1.4 Regulatory Setting ..................................................................................................................................7 2 BACKGROUND RESEARCH ............................................................................................................................. 13

2.1 Cultural Resources Records Search................................................................................................... 13

2.2 Building Development Research ........................................................................................................ 14 3 HISTORICAL CONTEXT .................................................................................................................................... 17

3.1 Prehistoric and Ethnographic Overview ............................................................................................. 17

3.2 Historical Overview of City of Glendora .............................................................................................. 17

3.3 Project Area History ............................................................................................................................. 21

3.4 Associated Engineer: Robert Bernard Diemer (1888-1966)............................................................ 28

3.5 Associated People: Judge Charles Silent (1842-1918) .................................................................... 29 4 HISTORIC RESOURCES SURVEY ..................................................................................................................... 31

4.1 Methods ............................................................................................................................................... 31

4.2 Results ................................................................................................................................................. 31 5 SIGNIFICANCE EVALUATIONS ......................................................................................................................... 33

5.1 Rancho Los Alisos/Camp Aventura Buildings and Structures.......................................................... 33

5.2 USFS and LACFCD concrete crib dams and channel structures ...................................................... 45

5.3 MWD Upper Feeder Pipeline segment (Monrovia No. 1) and Above-ground Structures ................ 51

5.4 Summary of Evaluation Findings........................................................................................................ 56 6 FINDINGS AND CONCLUSIONS ....................................................................................................................... 57

6.1 Summary of Findings .......................................................................................................................... 57

6.2 Consideration of Adverse Effects to Historic Properties.............................................................................. 57

6.3 Management Recommendations....................................................................................................... 59 7 BIBLIOGRAPHY................................................................................................................................................ 61

APPENDICES
A Preparer’s Qualifications
B Confidential Records Search Results
C DPR forms
D MWD Letter
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FIGURES
1 Project vicinity ......................................................................................................................................................3 2 APE map ...............................................................................................................................................................5 3 Plan of the Asuza Rancho in Los Angeles County owned by Henry Dalton, pre-1860. (Maps, Huntington Digital Library) ................................................................................................................... 19 4 Birds Eye View of Glendora, ca. 1910 (LAPL).................................................................................................. 20 5 Floor plan: Sheet no. 2 May 22, 1908. "Walls battered as directed". (NYDA.1960.001.03529, Greene & Greene Architectural Records & Paper Collections, Avery Architectural & Fine Arts Library)...... 22 6 Postcard of Rancho Los Alisos ranch house building group. (Silent Ranch subject files, Glendora Historical Society) ............................................................................................................................. 23 7 View to main buildings of Rancho Los Alisos, looking southwest, c 1910 (Oversized photos, Glendora Historical Society) ............................................................................................. 24 8 Colorado River Aqueduct Map, The Metropolitan Water District of Southern California. (Special Collections, Honnold Mudd Library, Claremont Colleges Library system)....................................... 26 9 Glendora Tunnel section of the Foothill Feeder, 1965. (Los Angeles Herald Examiner Photo Collection, Los Angeles Public Library)............................................................................................ 27 10 USFS employees constructing a concrete crib dam north of Glendora. (Los Angeles Times 1970)......... 28 11 Left: Rock wall and bench feature (IMG_4041); Right: 1910 photo of rock lined road and bench (Glendora Historical Society)............................................................................................................................ 34 12 Another segment of rock-line road (IMG 4003) .............................................................................................. 34 13 Left: concrete pool, looking southeast (IMG_4054); Right: 1910 photo of bass pool (Glendora Historical Society)............................................................................................................................ 35 14 Profile view of pool feature wall (IMG 1350).................................................................................................. 35 15 Entrance to rock “cave” showing rock walls sloping away, view to west (IMG_4051) ................................. 36 16 Stairs and retaining wall immediately right (northwest) of cave (IMG_1377) .............................................. 37 17 Left: view of steps looking northeast (IMG_1357); Right: 1910 postcard of fountain pavilion. (Glendora Historical Society)............................................................................................................................ 38 18 Left: view of steps looking northeast (IMG_2394); Right: 1910 postcard of steps leading to earthen pavilion. (Glendora Historical Society)............................................................................................... 39 19 View of steps looking south (IMG 4006) ........................................................................................................ 39 20 Main and west elevations of restroom building, view to southeast (IMG_4010) ......................................... 40 21 West crib dam, with dam in background, concrete sill in foreground, looking northwest (IMG_1264) ...... 46 22 Center crib dam, looking north (IMG_1332) ................................................................................................... 47 23 East crib dam, looking north (IMG_1320)....................................................................................................... 48 24 Concrete lined channel, 550 feet south of dam, looking north (IMG_4019)................................................ 48 25 MWD hatch, looking northwest (IMG_1339)................................................................................................... 52 Item #8. Page 857
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TABLES
1 Previously Conducted Technical Studies within 0.5-Mile of the Proposed Project APE ............................... 13 2 Previously Recorded Resources within 0.5-Mile of the Proposed Project APE ............................................. 14 3 Built Environment: Summary of Findings for buildings and structures in the Proposed Project APE.......... 31 4 Application of Criteria of Adverse Effects for the Monrovia No. 1 tunnel and hatch within the Proposed Project APE................................................................................................................................. 58 Item #8. Page 858
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Executive Summary
Dudek was retained by City of Glendora Planning Department to prepare a historical significance evaluation report for an approximately 27-acre property located at 950 North Silent Ranch Drive in the City of Glendora, California (APN: 8684-045-004). The proposed project APE contains several buildings and structures over 45 years old that have not been previously evaluated for historical significance. This report includes a pedestrian survey of the property by a qualified architectural historian, a California Historical Resources Information System (CHRIS) records search of the APE and a 0.5-mile radius, building development and archival research, development of an appropriate historic context for the property, and evaluation of the property for historical significance and integrity in consideration of National Register of Historic Places (NRHP), California Register of Historical Resources (CRHR), and City of Glendora historic resources ad landmarks designation criteria. This report was prepared in conformance with California Environmental Quality Act (CEQA), and Section 106 of the National Historic Preservation Act (NHPA).

As a result of the CHRIS records search, extensive archival research with Glendora Historical Society, building permit history, field survey, and property significance evaluation, one historic property was identified within the APE: the Metropolitan Water District of Southern California (MWD) Upper Feeder pipeline and its associated concrete hatch structure. The MWD pipeline is recommended eligible under Criteria A/1/as a representative component of the MWD Upper Feeder pipeline, which was instrumental in delivery of Colorado River Water to the region, and the first multi-city municipal water distribution system of its kind. The period of significance for this historic property is 1931 to 1941. In consideration of these findings, the MWD pipeline and hatch structure are considered an historic property under Section 106 of the NHPA and an historical resource under CEQA. Impacts discussion, mitigation measures, and management recommendations are discussed in Section 6.

The remaining resources located at 950 North Silent Ranch Drive (APN: 8684-045-004): the Rancho Los Alisos Structures, Camp Aventura building, and joint Forest Service and County Flood Control District dams and channel do not appear not eligible for the NRHP, CRHR, or as a City of Glendora historic resource or landmark due to a lack of significant historical associations and architectural merit. Therefore, these resources are not considered historical resource for the purposes of CEQA. No management recommendations are required for these ineligible resources.

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1 Introduction
Dudek was retained by City of Glendora Planning Department to complete a historical significance evaluation report for an approximately 27-acre property located at 950 North Silent Ranch Drive in the City of Glendora, California (APN: 8684-045-004) (hereafter, proposed project APE). The proposed project APE contains several buildings and structures over 45 years old and has not been previously evaluated for historical significance. This report includes a pedestrian survey of the property by a qualified architectural historian, a California Historical Resources Information System (CHRIS) records search of the APE and a 0.5-mile radius, building development and archival research, development of an appropriate historic context for the property, and evaluation of the property for historical significance and integrity in consideration of National Register of Historic Places (NRHP), California Register of Historical Resources (CRHR), and City of Glendora historic resources ad landmarks designation criteria.

This report was prepared in conformance with California Environmental Quality Act (CEQA) Guidelines Section 15064.5 for historical resources and Section 106 of the National Historic Preservation Act (NHPA) for historic properties.

1.1 Project Description and Location
The Grand Estates Project (proposed project) would involve the subdivision of a hillside property in the City of Glendora for the development of 13 single-family residential lots and one private street. It is expected that 12 singlefamily homes would be constructed on the new lots (one lot has an existing home, to remain in place). The proposed project area of potential effect (APE) is approximately 27 acres in size and is located at 950 North Silent Ranch Drive, at the northern terminus of Grand Avenue in the City of Glendora (Figure 1. Project Vicinity). The majority of the proposed project APE is currently vacant and undeveloped, with the exception of one single-family residence and three flood control structures, which are intended to control debris flow from the hillside above. The existing single-family residence would remain in place, and the three existing flood control structures would be demolished and new debris basins and maintenance road would be constructed as part of the proposed project, to provide effective protection from debris flow and flooding.

1.2 Area of Potential Effects (APE)
The APE is the geographic area or areas within which an undertaking may directly or indirectly cause changes in the character or use of historic properties. Delineation of the APE is influenced by the project’s setting, the scale and nature of the undertaking, and the different kinds of effects that may result from the undertaking (36 Code of Federal Regulations [CFR] 800.16[d]). Specifically, the APE follows the maximum possible area for potential impacts resulting from the proposed project, including all ground disturbing activities related to construction, easements, and staging areas located in the proposed project APE. Potential ground disturbance ranges from 25 to 35 feet deep with at least five feet of over-excavation to compensate for irregularities in the subgrade. Therefore, the vertical APE is up to 40 feet. The proposed project would affect the buildings and structures at 950 North Silent Ranch Drive, Glendora California. (Figure 2. APE Map).

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Project Location
Historical Resources Technical Report for the Silent Ranch Hillside Subdivision Project SOURCE: USGS 7.5-Minute Series Azusa & Glendora Quadrangles Date: 8/20/2019 - Last saved by: bdokkestul - Path: Z:\Projects\j837501\MAPDOC\DOCUMENT\Cultural\HistoricalResources_TR\Figure1-ProjectLocation.mxd 02 1,000 ,000
Feet
Project Site Boundary
FIGURE 1
1:24,000
0 285 570Meters
Mission Viejo
Long
Beach
El
Segundo
Ontario
Eastvale
Culver City
Malibu Industry
Colton
Colton
El Monte Beverly Hills
San
Dimas
Agoura
Hills
Arcadia Glendora
Fontana Duarte
Pasadena
San Fernando
Hesperia
Hesperia
Hesperia
Santa Clarita
Victorville
Palmdale Adelanto
Lancaster
Rialto
San
Bernardino
Palos Verdes
Estates
Newport Beach
Santa Monica
Oxnard
Thousand Oaks
Moorpark
Fillmore
Ojai
Simi Valley
Los Angeles
Kern County
Ventura
County
Orange
County
101
395
48 71
57 118
134
91 103
39 55
159
23 73
241
232
187
126
170
213 22
90 34
83 150
27 18
1 66
19 60
14 2
138
10 405
5 210
5 710
15 605
105

LOS ANGELES
COUNTY
Project Site
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Project APE
Historical Resources Technical Report for the Silent Ranch Hillside Subdivision Project SOURCE: County of Los Angeles 2018; Bing Maps 2018; NHD 2018 Date: 8/21/2019 - Last saved by: bdokkestul - Path: Z:\Projects\j837501\MAPDOC\DOCUMENT\Cultural\HistoricalResources_TR\Figure2_ProjectAPE.mxd 0 100 200Feet
Proposed Project APE
Rancho Los Alisos/Camp Aventura
MWD Upper Feeder Hatch
USFS/LACFCD Crib Dam
USFS/LACFCD Flood Control Channel
Rancho Los Alisos/Camp Aventura
MWD Upper Feeder pipeline
FIGURE 2
1:2,400
05 25 0
Meters
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1.3 Project Personnel
This report and associated property evaluation was prepared by Dudek Architectural Historian Kate Kaiser, MSHP.

The report was reviewed for quality assurance/quality control by Dudek Senior Architectural Historians Kathryn Haley, MA and Samantha Murray, MA. All authors and reviewers meet the Secretary of the Interior’s Professional Qualification Standards (36 CFR Part 61) for architectural history or archaeology (see Appendix A, Preparers’ Qualifications).

1.4 Regulatory Setting
National Historic Preservation Act
The NHPA established the NRHP and the President’s Advisory Council on Historic Preservation (ACHP), and provided that states may establish State Historic Preservation Officers (SHPOs) to carry out some of the functions of the NHPA. Most significantly for federal agencies responsible for managing cultural resources, Section 106 of the NHPA directs that “[t]he head of any Federal agency having direct or indirect jurisdiction over a proposed Federal or federally assisted undertaking in any State and the head of any Federal department or independent agency having authority to license any undertaking shall, prior to the approval of the expenditure of any Federal funds on the undertaking or prior to the issuance of any license, as the case may be, take into account the effect of the undertaking on any district, site, building, structure, or object that is included in or eligible for inclusion in the NRHP.” Section 106 also affords the ACHP a reasonable opportunity to comment on the undertaking (16 U.S. Code 470f).

The content of 36 Code of Federal Regulations, Part 800 (36 CFR 800) implements Section 106 of the NHPA. It defines the steps necessary to identify historic properties (those cultural resources listed in or eligible for listing in the NRHP), including consultation with federally recognized Native American tribes to identify resources with important cultural values; to determine whether or not they may be adversely affected by a proposed undertaking; and to outline the process for eliminating, reducing, or mitigating the adverse effects.

The ACHP provides methodological and conceptual guidance for identifying historic properties. In 36 CFR 800.4, the steps necessary for identifying historic properties are as follows:
• Determine and document the APE (36 CFR 800.16(d)).
• Review existing information on historic properties within the APE, including preliminary data. • Confer with consulting parties to obtain additional information on historic properties or concerns about effects to these.
• Consult with Native American tribes (36 CFR 800.3(f)) to obtain knowledge on resources that are identified with places where they attach cultural or religious significance. • Perform appropriate fieldwork (including phased identification and evaluation). • Apply NRHP criteria to determine resource eligibility for NRHP listing.

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Fulfilling these steps is generally thought to constitute a reasonable effort to identify historic properties within the APE for an undertaking. The obligations of a federal agency must also assess whether an undertaking will have an adverse effect on cultural resources. An undertaking will have an adverse effect when:
an undertaking may alter, directly or indirectly, any of the characteristics of a historic property that qualify the property for inclusion in the National Register in a manner that would diminish the integrity of the property's location, design, setting, materials, workmanship, feeling, or association.

Consideration shall be given to all qualifying characteristics of a historic property, including those that may have been identified subsequent to the original evaluation of the property’s eligibility for the National Register. Adverse effects may include reasonably foreseeable effects caused by the undertaking that may occur later in time, be farther removed in distance or be cumulative” (36 CFR Part 800.5(1)).

The process of determining whether an undertaking may have an adverse effect requires the federal agency to confer with consulting parties to appropriately consider all relevant stakeholder concerns and values. Consultation regarding the treatment of a historic property may result in a Programmatic Agreement and/or Memorandum of Agreement between consulting parties that typically include the lead federal agency, SHPO, and other applicable parties if they agree to be signatories to these documents. Treatment documents—whether resource-specific or generalized—provide guidance for resolving potential or realized adverse effects to known historic properties or to those that may be discovered during implementation of an undertaking. In all cases, avoidance of adverse effects to historic properties is the preferred treatment measure, and it is generally the burden of the federal agency to demonstrate why avoidance may not be feasible.

Federal
National Register of Historic Places
The NRHP is the United States’ official list of districts, sites, buildings, structures, and objects worthy of preservation.

Overseen by the National Park Service, under the U.S. Department of the Interior, the NRHP was authorized under the National Historic Preservation Act, as amended. Its listings encompass all National Historic Landmarks, as well as historic areas administered by the National Park Service.

NRHP guidelines for the evaluation of historic significance were developed to be flexible and to recognize the accomplishments of all who have made significant contributions to the nation’s history and heritage. Its criteria are designed to guide state and local governments, federal agencies, and others in evaluating potential entries in the NRHP. For a property to be listed in or determined eligible for listing, it must be demonstrated to possess integrity and to meet at least one of the following criteria:

The quality of significance in American history, architecture, archaeology, engineering, and culture is present in districts, sites, buildings, structures, and objects that possess integrity of location, design, setting, materials, workmanship, feeling, and association, and:

A. That are associated with events that have made a significant contribution to the broad patterns of our history; or
B. That are associated with the lives of persons significant in our past; or Item #8. Page 869
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C. That embody the distinctive characteristics of a type, period, or method of construction, or that represent the work of a master, or that possess high artistic values, or that represent a significant and distinguishable entity whose components may lack individual distinction; or D. That have yielded, or may be likely to yield, information important in prehistory or history.

Integrity is defined in NRHP guidance, “How to Apply the National Register Criteria,” as “the ability of a property to convey its significance. To be listed in the NRHP, a property must not only be shown to be significant under the NRHP criteria, but it also must have integrity” (NPS 1990). NRHP guidance further asserts that properties be completed at least 50 years ago to be considered for eligibility. Properties completed fewer than 50 years before evaluation must be proven to be “exceptionally important” (criteria consideration to be considered for listing.

State
California Register of Historical Resources
In California, the term “historical resource” includes but is not limited to “any object, building, structure, site, area, place, record, or manuscript which is historically or archaeologically significant, or is significant in the architectural, engineering, scientific, economic, agricultural, educational, social, political, military, or cultural annals of California” (California Public Resources Code Section 5020.1(j)). In 1992, the California legislature established the California Register of Historical Resources (CRHR) “to be used by state and local agencies, private groups, and citizens to identify the state’s historical resources and to indicate what properties are to be protected, to the extent prudent and feasible, from substantial adverse change” (California Public Resources Code Section 5024.1(a)). The criteria for listing resources on the CRHR were expressly developed to be in accordance with previously established criteria developed for listing in the NRHP, enumerated below. According to California Public Resources Code Section 5024.1(c)(1–4), a resource is considered historically significant if it (i) retains “substantial integrity,” and (ii) meets at least one of the following criteria:

Is associated with events that have made a significant contribution to the broad patterns of California’s history and cultural heritage.
(1) Is associated with events that have made a significant contribution to the broad patterns of California’s history and cultural heritage.
(2) Is associated with the lives of persons important in our past. (3) Embodies the distinctive characteristics of a type, period, region, or method of construction, or represents the work of an important creative individual, or possesses high artistic values. (4) Has yielded, or may be likely to yield, information important in prehistory or history.

In order to understand the historic importance of a resource, sufficient time must have passed to obtain a scholarly perspective on the events or individuals associated with the resource. A resource less than 50 years old may be considered for listing in the CRHR if it can be demonstrated that sufficient time has passed to understand its historical importance (see 14 CCR 4852(d)(2)).

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The CRHR protects cultural resources by requiring evaluations of the significance of prehistoric and historic resources. The criteria for the CRHR are nearly identical to those for the NRHP, and properties listed or formally designated as eligible for listing in the NRHP are automatically listed in the CRHR, as are the state landmarks and points of interest. The CRHR also includes properties designated under local ordinances or identified through local historical resource surveys.

California Environmental Quality Act
As described further below, the following CEQA statutes and CEQA Guidelines are of relevance to the analysis of archaeological, historic, and tribal cultural resources:
• California Public Resources Code Section 21083.2(g) defines “unique archaeological resource.” • California Public Resources Code Section 21084.1 and CEQA Guidelines Section 15064.5(a) define “historical resources.” In addition, CEQA Guidelines Section 15064.5(b) defines the phrase “substantial adverse change in the significance of an historical resource.” It also defines the circumstances when a project would materially impair the significance of an historical resource. • California Public Resources Code Section 21074(a) defines “tribal cultural resources.” • California Public Resources Code Section 5097.98 and CEQA Guidelines Section 15064.5(e) set forth standards and steps to be employed following the accidental discovery of human remains in any location other than a dedicated ceremony.
• California Public Resources Code Sections 21083.2(b)-(c) and CEQA Guidelines Section 15126.4 provide information regarding the mitigation framework for archaeological and historic resources, including examples of preservation-in-place mitigation measures; preservation-in-place is the preferred manner of mitigating impacts to significant archaeological sites because it maintains the relationship between artifacts and the archaeological context and may also help avoid conflict with religious or cultural values of groups associated with the archaeological site(s).

More specifically, under CEQA, a project may have a significant effect on the environment if it may cause “a substantial adverse change in the significance of an historical resource” (California Public Resources Code Section 21084.1; CEQA Guidelines Section 15064.5(b).) If a site is either listed or eligible for listing in the CRHR, or if it is included in a local register of historic resources or identified as significant in a historical resources survey (meeting the requirements of California Public Resources Code Section 5024.1(q)), it is a “historical resource” and is presumed to be historically or culturally significant for purposes of CEQA (California Public Resources Code Section 21084.1; CEQA Guidelines Section 15064.5(a)). The lead agency is not precluded from determining that a resource is a historical resource even if it does not fall within this presumption (California Public Resources Code Section 21084.1; CEQA Guidelines Section 15064.5(a)).

A “substantial adverse change in the significance of an historical resource” reflecting a significant effect under CEQA means “physical demolition, destruction, relocation, or alteration of the resource or its immediate surroundings such that the significance of an historical resource would be materially impaired” (CEQA Guidelines Section 15064.5(b)(1); California Public Resources Code Section 5020.1(q)). In turn, CEQA Guidelines section 15064.5(b)(2) states the significance of an historical resource is materially impaired when a project:

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1. Demolishes or materially alters in an adverse manner those physical characteristics of an historical resource that convey its historical significance and that justify its inclusion in, or eligibility for, inclusion in the California Register of Historical Resources; or

2. Demolishes or materially alters in an adverse manner those physical characteristics that account for its inclusion in a local register of historical resources pursuant to section 5020.1(k) of the Public Resources Code or its identification in an historical resources survey meeting the requirements of section 5024.1(g) of the Public Resources Code, unless the public agency reviewing the effects of the project establishes by a preponderance of evidence that the resource is not historically or culturally significant; or

3. Demolishes or materially alters in an adverse manner those physical characteristics of a historical resource that convey its historical significance and that justify its eligibility for inclusion in the California Register of Historical Resources as determined by a lead agency for purposes of CEQA.

Pursuant to these sections, the CEQA inquiry begins with evaluating whether a project site contains any “historical resources,” then evaluates whether that project will cause a substantial adverse change in the significance of a historical resource such that the resource’s historical significance is materially impaired.

If it can be demonstrated that a project will cause damage to a unique archaeological resource, the lead agency may require reasonable efforts be made to permit any or all of these resources to be preserved in place or left in an undisturbed state. To the extent that they cannot be left undisturbed, mitigation measures are required (California Public Resources Code Section 21083.2[a], [b], and [c]).

California Public Resources Code Section 21083.2(g) defines a unique archaeological resource as an archaeological artifact, object, or site about which it can be clearly demonstrated that without merely adding to the current body of knowledge, there is a high probability that it meets any of the following criteria:

1. Contains information needed to answer important scientific research questions and that there is a demonstrable public interest in that information.

2. Has a special and particular quality such as being the oldest of its type or the best available example of its type.

3. Is directly associated with a scientifically recognized important prehistoric or historic event or person.

Impacts to non-unique archaeological resources are generally not considered a significant environmental impact (California Public Resources Code section 21083.2(a); CEQA Guidelines Section 15064.5(c)(4)). However, if a nonunique archaeological resource qualifies as tribal cultural resource (California Public Resources Code Section 21074(c), 21083.2(h)), further consideration of significant impacts is required. CEQA Guidelines Section 15064.5 assigns special importance to human remains and specifies procedures to be used when Native American remains are discovered. As described below, these procedures are detailed in California Public Resources Code Section 5097.98.

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Local
City of Glendora (21.03.050 Historic preservation).

The most recent iteration of the City of Glendora’s historic preservation ordinance was adopted in 2014. The ordinance established the purpose, roles, and responsibilities of the Historic Preservation Commission, along with nomination and designation program for historic resources. Historic resources or landmarks shall be designated based upon one or more of the following findings:

1. The proposed preserved features exemplify or reflect special elements of historical, architectural, archaeological, cultural, or aesthetic heritage.

2. The proposed preserved features are identified with persons or events significant in local, state, or national history.

3. The proposed features embody distinctive characteristics of a style, type, period or method of construction or are valuable examples of the use of indigenous materials or craftsmanship.

4. The proposed preserved features are representative of the notable work of a builder, designer or architect.

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2 Background Research

2.1 Cultural Resources Records Search
On June 28, 2019, Dudek completed a search of the CHRIS at the SCCIC, located on the campus of California State University, Fullerton of the proposed project APE and a half (0.5) mile buffer. This search included mapped prehistoric and historic archaeological resources and historic built-environment resources; Department of Parks and Recreation site records; technical reports; archival resources; and ethnographic references. Additional consulted sources included historical maps of the proposed project APE, the NRHP, the CRHR, the California Historic Property Data File, and the lists of California State Historical Landmarks, California Points of Historical Interest, and the Archaeological Determinations of Eligibility. The confidential records search results are also provided in Appendix B.

Previously Conducted Cultural Resource Studies
The SCCIC records indicate that seven (7) previous cultural resources technical investigations have been conducted within 0.50mile of the proposed project APE between 1988 and 2019. All seven technical investigations and are summarized in Table 1.

Table 1. Previously Conducted Technical Studies within 0.5-Mile of the Proposed Project APE Report
Number Author Year Report Title
Within the Project APE
LA-00837 Cottrell, Marie G. 1977 An Archaeological Survey Conducted on a Parcel of Land North of Palm Drive in the City of Glendora, Los Angeles County, California
Outside the Project APE
LA-00334 Desautels, Roger J. 1978 Archaeological Survey Report on Tentative Tract No. 33742 Located in the City of Glendora, County of Los Angeles.

LA-01439 Cottrell, Marie G. 1985 Archaeological Resources Assessment of the Azusa Pacific University Hillside Campus in the City of Glendora, California
LA-08068 Wlodarski, Robert J. 1996 Draft Report: Peer Review of the Monrovia Nursery Project Cultural Resources Element
LA-08073 Farrell, Nancy 1992 Monrovia Nursery Project Cultural Resources Investigation LA-10172 Brasket, Kelli S. 2006 Glendora Ridge Motorway and Van Tassel Road Maintenance Project LA-10579 Hunt, Kevin and
Patrick Maxon
2006 Final- Cultural Resources Survey for the Monrovia Nursery Development Project, Glendora, Los Angeles County, California
Source: SCCIC visit by Dudek staff 8/28/2019
LA-00837
An Archaeological Survey Conducted on a Parcel of Land North of Palm Drive in the City of Glendora, Los Angeles County, California (Cottrell 1977) was an archaeological survey report conducted on the proposed project APE parcel in November 1977, prior to grading a portion of the site in anticipation of a residential development project.

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basins. The report does not record any historical features, but noted their presence and association either to the Silent Ranch/Rancho Los Alisos property or to the Girl Scout camp.

Previously Recorded Cultural Resources
The SCCIC records indicate that two cultural resources have been recorded within 0.5-mile of the proposed project APE; neither of which overlap or are located adjacent to the proposed project APE. One resource is the Angeles National Forest, which encompasses the entirety of the forest and one resource is a historic road. Both resources are summarized in Table 2.

Table 2. Previously Recorded Resources within 0.5-Mile of the Proposed Project APE Primary
Number Trinomial Period NRHP Status Description Recorded by/Year Outside the Project APE
P-19-
186535
n/a Historic 7L: State Historical Landmarks 1-769 and
Points of Historical Interest designated prior to
January 1998 – Needs to be reevaluated
using current standards; CHL # 717
Historic Site:

Angeles National
Forest
1979 (J. Arbuckle)
P-19-
188290
n/a Historic Not evaluated Historic Structure:

Glendora Ridge
Motorway
2005 (Brasket, K., J.

Huckabee, and D.

Peebles)
Source: SCCIC visit by Dudek staff 8/28/2019

2.2 Building Development Research
Los Angeles County Assessor
Dudek accessed the Los Angeles County Tax Assessor’s online Property Assessment Information System (PAIS) on August 15, 2019. The available reports from PAIS provided property information that included dates of construction.

The information from PAIS was used in the preparation of the historic context.

City of Glendora eTRAKit Online Permit System
Dudek accessed the City of Glendora’s online permitting system (eTRAKit) on August 14 and 15, 2019. Dudek collected permit information for 950 N Silent Ranch Drive and 935 N. Silent Ranch Drive (which contained information about the Aventura Girl Scout Camp). The available reports from PAIS provided property information that included dates of construction and alterations for structures built after 1950. The information from eTRAKit was used in the preparation of the historic context and identified alterations sections.

City of Glendora Public Library
On August 16, 2019, Dudek visited the Glendora Public Library to review sources relating to the history of Glendora.

These collections included photographs, books, and maps. Research at the Glendora Public Library was used in the preparation of the historic context.

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Glendora Historical Society
On August 20, 2019, Dudek visited the Glendora Historical Society Museum to review items in the museum collection relating to the history of Glendora and collections for Silent Ranch. These collections included photographs, books, notebooks, pamphlets, advertisements, newspaper clippings and other archival materials.

Research at the Glendora Historical Society was used in the preparation of the historic context.

Aerial Photograph Review
Historic aerial photographs of the proposed project APE were available from Nationwide Environmental Title Research (NETR) LLC maps for the years 1953, 1964, 1965, 1972, 1977, 1978, 1980, 1994, 2002, 2003, 2004, 2005, 2009, 2012, and 2014, and from the University of California Santa Barbara (UCSB) Map and Imagery Laboratory for the years 1927, 1933, 1934, 1938, 1949, 1953, 1954, 1956, 1960, 1964, 1968, 1976, 1981 (NETR 2019a; UCSB 2019).

The earliest aerial photographs from 1927 show Judge Charles Silent’s Rancho Los Alisos. A circular fountain feature is located in the southeastern portion of the property, while the main house, outbuildings, and lawns are located loser to the western property boundary. The property is framed to the north by the vegetation at the base of the foothills. Some features appear in this vegetated area, such as a road cuts, footpaths, tree border, and a water cistern. The rest of the property is dominated by an evenly spaced, mature orchard.

The proposed project APE and surrounding area do not noticeably change in appearance or layout until the 1954 photograph. In the 1953 photograph the orchards that dominate the area south of the main house are present and densely arranged. In the 1954 photograph, some of the trees have been removed. By the 1956 aerial photograph, all of the orchard trees except two rows along the southern boundary on Palm Drive were removed. The tree lined access road was retained and a palm tree surrounded fountain/water feature in the southeastern property corner appears dry and infilled.

In the 1960 photograph, four buildings, and ten tent pads arranged in semi circles around the buildings appear in the southern section of the property, likely related to the Camp Aventura Girl Scout Camp. The northwestern corner of the property appears to have been subdivided into a separate property and in 1960 has a large, rectangular plan building with pool, driveway and fence along the property line. Another square plan building, located just north of the vegetated area in the northern portion of the property, also appears in the 1960 photograph, with a separate driveway leading to it. A large, square parking lot also appears in the southwestern corner of the property. Around the property is the Girls’ School to the west and several sports fields, but south of Palm Drive and east of Grand Avenue several residential subdivisions appear mid-construction. By the 1968 photograph, the water feature in the southeastern portion of the property appears overgrown. A fifth, very large irregular plan building appears north of the Camp Aventura buildings, as well as formal footpaths to the camp buildings and a separate driveway. Perhaps most meaningfully, the original Charles Silent Rancho Los Alisos-era ranch house and outbuildings are all removed in the 1968 photograph. By the 1976 photograph, a new house is under construction in the same location as the demolished Rancho Los Alisos-era house. The tent pads are no longer present at the Camp Aventura buildings and the paths between camp buildings appear disused and grown over. The large, rectangular-plan property just west also appears to have been demolished. The three concrete debris dams, and the concrete lined channel leading south from the east-most debris dam, are visible in the 1976 photograph. West of the proposed project APE and the Girls’ School buildings is the Hook Canyon debris dam and channel a significantly larger Los Angeles County Flood Control District debris dam, concrete lined flood control channel, and water tanks.

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By the 1981 photograph, there are again drastic changes to the property. All of the visible Camp Aventura buildings appear demolished and land leveled, in the southern portion of the property, along Palm Drive. The square plan building situated in the vegetation in the western portion of the property appears demolished. The new ranch house building appears completed, and has a pool house, pool, and landscaped lawns and small immature orchard, northwest of the building. In the 1982 photograph, individual lot foundations and an access road are visibly under construction, creating a residential subdivision with 15 lots. By the next available photograph from 1994 and 1995, some, but not all lots appear to have construction activity and new buildings on them. By the 2003 photograph, all of the lots are filled. There are few other changes to the proposed project APE after 2003. Between the 2012 and 2014 photograph, the vegetation appears to have reduced in the canyon drainages, suggesting a fire.

Historical Map Review
A review of historic maps and aerial photographs was conducted as part of the archival research effort for the project. Sanborn Fire Insurance Company Maps were prepared for the City for the years 1910, 1928, and 1931; however, their coverage did not extend to the proposed project APE. An adjacent property, the Girls Collegiate School is on the 1931 Sanborn map, but no data for the proposed project APE is given. Topographic maps are available from NETR for the years 1897, 1898, 1902, 1904, 1908, 1912, 1923, 1925, 1927, 1932, 1933, 1939, 1941, 1946, 1955, 1957, 1960, 1964, 1968, 1975, 1999, 2012, and 2015. Additional topographic maps were available from the interactive USGS Historical Topographic Map Explorer website for the years 1894, 1897, 1897, 1901, 1904, 1925, 1927, 1933, 1939, 1953, 1966, 1972, and 1995.

The earliest topographical maps from 1894, 1897, and 1898 show two properties, marked by solid black squares near the northern terminus of Grand Avenue. There are few other markings in the proposed project APE, but the city boundaries of Glendora move incrementally north and west towards the proposed project APE until 1927, when four more structure symbols appear near the Grand Avenue terminus. Far north of the proposed project APE, the Morris Dam appears along the San Gabriel River, the major watershed of the area, creating a dam and several aqueducts in the area. In the 1939 topographic map, a water feature called the Metropolitan Aqueduct (Metropolitan Water District (MWD) Upper Feeder) appears in this topographic map for the first time, bisecting the proposed project APE. Six springs are also marked in the foothills northwest, north and northeast of the proposed project APE. The proposed project APE appears to have three structures, an unpaved road and a water reservoir on it. The Girls Collegiate School campus (later St. Lucy’s Priory School) appears north of the intersection of Barranca Avenue and Sierra Madre Avenue, west of the proposed project APE. In the 1966 topographic map, the Camp Aventura Girl Scout Camp appears. Also by the 1966 topographic map, the proposed project APE no longer appears to be on the rural fringes of Glendora, but rather a developed suburban community within the Glendora development limits. There are no radical changes to the proposed project APE or surrounding neighborhood after this according to topographical maps (NETR 2019b; USGS 2019).

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3 Historical Context

3.1 Prehistoric and Ethnographic Overview
Prehistoric
Numerous chronological sequences have been devised to aid in understanding cultural changes within southern California. Building on early studies and focusing on data synthesis, Wallace (1955, 1978) developed a prehistoric chronology for the Southern California coastal region that is still widely used today and is applicable to near-coastal and many inland areas. Four periods are presented in Wallace’s prehistoric sequence: Early Man (Horizon I), Milling Stone (Horizon II), Intermediate (Horizon III), and Late Prehistoric (Horizon IV). The earliest accepted dates for occupation are from two of the northern Channel Islands, located off the coast of Santa Barbara. On San Miguel Island, Daisy Cave clearly establishes the presence of people in this area about 10,000 years ago (Erlandson 1991).

Recent data from Horizon I sites indicate that the economy was a diverse mixture of hunting and gathering, with a major emphasis on aquatic resources in many coastal areas and on Pleistocene lakeshores in eastern San Diego County (see Moratto 1984). The Milling Stone Horizon of Wallace (1955, 1978) and Encinitas Tradition of Warren (1968) (6000–3000 BC) are characterized by subsistence strategies centered on collecting plant foods and small animals. Following the Milling Stone Horizon, Wallace’s Intermediate Horizon and Warren’s Campbell Tradition in Santa Barbara, Ventura, and parts of Los Angeles Counties, date from approximately 3000 BC to AD 500 and are characterized by a shift toward a hunting and maritime subsistence strategy, along with a wider use of plant foods.

In the Late Prehistoric Horizon (Wallace 1955, 1978), which lasted from the end of the Intermediate (ca. AD 500) until European contact, there was an increase in the use of plant food resources in addition to an increase in land and sea mammal hunting. There was a concomitant increase in the diversity and complexity of material culture during the Late Prehistoric.

Ethnographic
The proposed project APE is in an area historically occupied by the Gabrielino. The archaeological record indicates that the Gabrielino arrived in the Los Angeles Basin around 500 BC. Many contemporary Gabrielino identify themselves as descendants of the indigenous people living across the plains of the Los Angeles Basin and adjacent areas. The name “Gabrielino” denotes those people who were administered by the Spanish from the San Gabriel Mission, which included people from the Gabrielino area proper as well as other social groups (Bean and Smith 1978; Kroeber 1925). Many modern Gabrielino identify themselves as descendants of the indigenous people living across the plains of the Los Angeles Basin and refer to themselves as the Tongva (King 1990), while others reject this term. Gabrielino lands encompassed the greater Los Angeles Basin and three Channel Islands, San Clemente, San Nicolas, and Santa Catalina. The Gabrielino established large, permanent villages in the fertile lowlands along rivers and streams, and in sheltered areas along the coast, stretching from the foothills of the San Gabriel Mountains to the Pacific Ocean. A total tribal population has been estimated of at least 5,000 (Bean and Smith 1978), but recent ethnohistoric work suggests a number approaching 10,000 (O’Neil 2002).

3.2 Historical Overview of City of Glendora
The historical period for the state of California is generally divided into three periods: the Spanish Period (1769– 1822), Mexican Period (1822–1848), and American Period (1848–present). Although Spanish, Russian, and Item #8. Page 878
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British explorers visited the area for brief periods between 1529 and 1769, the Spanish Period in California begins with the establishment in 1769 of a settlement at San Diego and the founding of Mission San Diego de Alcalá, the first of 21 missions constructed between 1769 and 1823. In 1771, a fourth mission was founded at the Mission San Gabriel Arcángel by a Portola expedition. The original 1771 mission was destroyed in a flash flood and a new mission was built in 1776. El Pueblo de Nuestra Señora la Reina de Los Ángeles, further west, was established in 1781 to support Mission San Gabriel Arcángel. The San Gabriel Mission lands extended from Los Angeles east as far as San Bernardino de Sena Estancia (established 1810), and the San Bernardino Valley, including present day Irwindale, would have been under Mission San Gabriel Arcángel control (Caughey and Caughey 1977; Gumprecht 2001).

After more than a decade of intermittent rebellion and warfare, New Spain (Mexico and the California territory) won independence from Spain in 1821. In 1822, the Mexican legislative body in California ended isolationist policies designed to protect the Spanish monopoly on trade, and decreed California ports open to foreign merchants.

Mexican governors established extensive land grants throughout interior California during the Mexican Period, in part to wrest secular control away from the Spanish Missions and to give land as a reward to soldiers in lieu of pension. Land grants were also a way to disperse the population away from the more settled coastal areas and take advantage of cattle and agricultural industry (Dallas 1955; Fogelson 1993).

Mexican governors established extensive land grants throughout interior California during the Mexican Period, in part to wrest secular control away from the Spanish Missions and to give land as a reward to soldiers in lieu of pension. Land grants were also a way to disperse the population away from the more settled coastal areas and take advantage of cattle and agricultural industry. Mexican governor Juan Alvarado awarded Rancho El Susa to Luis Arenas and Rancho Azusa de Duarte to Andres Duarte in 1841. Just three years later, in 1844 Arenas sold onethird interest in Rancho San Jose to Englishman and merchant Henry Dalton. Dalton also acquired the San Jose Addition, and Rancho Azusa in 1844, and renamed his acquired lands Rancho Azusa de Dalton (Figure 3) (Caughey and Caughey 1977; Dallas 1955; Lewis Publishing Co. 1889; Zerneke 2009).

Item #8. Page 879
Meeting Date: 1/24/2023 / Packet Page #: 944

HISTORICAL RESOURCES TECHNICAL REPORT FOR

GRAND ESTATES PROJECT
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Figure 3. Plan of the Asuza Rancho in Los Angeles County owned by Henry Dalton, pre-1860. (Maps, Huntington Digital Library)
The Mexican Period ended with the signing of the Treaty of Guadalupe Hidalgo in 1848, ending the MexicanAmerican War, which signals the beginning of the American Period when California became a territory of the United States. California officially became a state with the Compromise of 1850, which also designated Utah and New Mexico (with present-day Arizona) as U.S. Territories. After the Treaty of Guadalupe Hidalgo in 1848, Henry Dalton lost the majority of his assets and was forced to live the rest of his life in poverty (City of Glendora 1999; Lewis Publishing Co. 1889; Waugh 2003).

Dalton’s claims were partitioned and sold off and in the 1860s four homesteads along the foothills belonging to John Gassaway, John Harrar, Coleman Barnes, and Leonidas Barnes were recorded. In 1874, John Bender and William Bryant Cullen homesteaded 160 acres within what would become Glendora. They were soon joined by other homesteading families including Shorey, Preston, Wright, Griece, Washburn, Englehart, LaFetra, Johnson, and West.

The homesteads produced wheat, flax, barley, caster beans, potatoes other vegetables, grapevine orchards and fruit trees. Crops were sold in markets in either Los Angeles or San Bernardino, both near 2-days wagon ride away.

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