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Vicinity Map
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SEE FIS REPORT FOR DETAILED LEGEND AND INDEX MAP FOR FIRM PANEL LAYOUT
SPECIAL FLOOD
HAZARD AREAS
Without Base Flood Elevation (BFE)
Zone A, V, A99
With BFE or Depth Zone AE, AO, AH, VE, AR
Regulatory Floodway
0.2% Annual Chance Flood Hazard, Areas
of 1% annual chance flood with average
depth less than one foot or with drainage
areas of less than one square mile
Zone X
Future Conditions 1% Annual
Chance Flood Hazard
Zone X
Area with Reduced Flood Risk due to
Levee. See Notes.
Zone X
Area with Flood Risk due to LeveeZone D
NO SCREEN Area of Minimal Flood Hazard Zone X
Area of Undetermined Flood Hazard Zone D
Channel, Culvert, or Storm Sewer
Levee, Dike, or Floodwall
Cross Sections with 1% Annual Chance
17.5 Water Surface Elevation
Coastal Transect
Coastal Transect Baseline
Profile Baseline
Hydrographic Feature
Base Flood Elevation Line (BFE)
Effective LOMRs
Limit of Study
Jurisdiction Boundary
Digital Data Available
No Digital Data Available
Unmapped
This map complies with FEMA's standards for the use of
digital flood maps if it is not void as described below.
The basemap shown complies with FEMA's basemap
accuracy standards
The flood hazard information is derived directly from the authoritative NFHL web services provided by FEMA. This map was exported on 3/17/2025 at 11:11 PM and does not
reflect changes or amendments subsequent to this date and time. The NFHL and effective information may change or
become superseded by new data over time.
This map image is void if the one or more of the following map elements do not appear: basemap imagery, flood zone labels, legend, scale bar, map creation date, community identifiers, FIRM panel number, and FIRM effective date. Map images for unmapped and unmodernized areas cannot be used for
regulatory purposes.
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OTHER AREAS OF
FLOOD HAZARD
OTHER AREAS
GENERAL
STRUCTURES
OTHER
FEATURES
MAP PANELS
% 20.2
The pin displayed on the map is an approximate
point selected by the user and does not represent
an authoritative property location.
:
1
:
1
Basemap Imagery Source: USGS National Map 2023
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Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/X1-Q25.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID X1
Area (ac) 2.39
Flow Path Length (ft) 585.93
Flow Path Slope (vft/hft) 0.0119
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.77
Soil Type 7
Design Storm Frequency 25-yr
Fire Factor 0
LID False
Output Results
Modeled (25-yr) Rainfall Depth (in) 6.8484
Peak Intensity (in/hr) 3.4883
Undeveloped Runoff Coefficient (Cu) 0.7035
Developed Runoff Coefficient (Cd) 0.8548
Time of Concentration (min) 7.0
Clear Peak Flow Rate (cfs) 7.1266
Burned Peak Flow Rate (cfs) 7.1266
24-Hr Clear Runoff Volume (ac-ft) 0.9857
24-Hr Clear Runoff Volume (cu-ft) 42935.1368
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/X1-Q50.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID X1
Area (ac) 2.39
Flow Path Length (ft) 585.93
Flow Path Slope (vft/hft) 0.0119
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.77
Soil Type 7
Design Storm Frequency 50-yr
Fire Factor 0
LID False
Output Results
Modeled (50-yr) Rainfall Depth (in) 7.8
Peak Intensity (in/hr) 4.2715
Undeveloped Runoff Coefficient (Cu) 0.761
Developed Runoff Coefficient (Cd) 0.868
Time of Concentration (min) 6.0
Clear Peak Flow Rate (cfs) 8.8618
Burned Peak Flow Rate (cfs) 8.8618
24-Hr Clear Runoff Volume (ac-ft) 1.1261
24-Hr Clear Runoff Volume (cu-ft) 49052.075
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/X1-Q100.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID X1
Area (ac) 2.39
Flow Path Length (ft) 585.93
Flow Path Slope (vft/hft) 0.0119
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.77
Soil Type 7
Design Storm Frequency 100-yr
Fire Factor 0
LID False
Output Results
Modeled (100-yr) Rainfall Depth (in) 8.7516
Peak Intensity (in/hr) 4.7926
Undeveloped Runoff Coefficient (Cu) 0.7902
Developed Runoff Coefficient (Cd) 0.8747
Time of Concentration (min) 6.0
Clear Peak Flow Rate (cfs) 10.0196
Burned Peak Flow Rate (cfs) 10.0196
24-Hr Clear Runoff Volume (ac-ft) 1.2672
24-Hr Clear Runoff Volume (cu-ft) 55199.9844
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/X2-Q25.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID X2
Area (ac) 1.31
Flow Path Length (ft) 332.24
Flow Path Slope (vft/hft) 0.0166
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.77
Soil Type 7
Design Storm Frequency 25-yr
Fire Factor 0
LID False
Output Results
Modeled (25-yr) Rainfall Depth (in) 6.8484
Peak Intensity (in/hr) 4.0859
Undeveloped Runoff Coefficient (Cu) 0.7507
Developed Runoff Coefficient (Cd) 0.8657
Time of Concentration (min) 5.0
Clear Peak Flow Rate (cfs) 4.6335
Burned Peak Flow Rate (cfs) 4.6335
24-Hr Clear Runoff Volume (ac-ft) 0.5404
24-Hr Clear Runoff Volume (cu-ft) 23539.3306
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/X2-Q50.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID X2
Area (ac) 1.31
Flow Path Length (ft) 332.24
Flow Path Slope (vft/hft) 0.0166
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.77
Soil Type 7
Design Storm Frequency 50-yr
Fire Factor 0
LID False
Output Results
Modeled (50-yr) Rainfall Depth (in) 7.8
Peak Intensity (in/hr) 4.6537
Undeveloped Runoff Coefficient (Cu) 0.7824
Developed Runoff Coefficient (Cd) 0.873
Time of Concentration (min) 5.0
Clear Peak Flow Rate (cfs) 5.3218
Burned Peak Flow Rate (cfs) 5.3218
24-Hr Clear Runoff Volume (ac-ft) 0.6173
24-Hr Clear Runoff Volume (cu-ft) 26888.8189
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/X2-Q100.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID X2
Area (ac) 1.31
Flow Path Length (ft) 332.24
Flow Path Slope (vft/hft) 0.0166
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.77
Soil Type 7
Design Storm Frequency 100-yr
Fire Factor 0
LID False
Output Results
Modeled (100-yr) Rainfall Depth (in) 8.7516
Peak Intensity (in/hr) 5.2214
Undeveloped Runoff Coefficient (Cu) 0.8091
Developed Runoff Coefficient (Cd) 0.8791
Time of Concentration (min) 5.0
Clear Peak Flow Rate (cfs) 6.013
Burned Peak Flow Rate (cfs) 6.013
24-Hr Clear Runoff Volume (ac-ft) 0.6946
24-Hr Clear Runoff Volume (cu-ft) 30258.856
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Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/P1-Q50.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID P1
Area (ac) 2.62
Flow Path Length (ft) 660.89
Flow Path Slope (vft/hft) 0.0087
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 25-yr
Fire Factor 0
LID False
Output Results
Modeled (25-yr) Rainfall Depth (in) 6.8484
Peak Intensity (in/hr) 3.2761
Undeveloped Runoff Coefficient (Cu) 0.686
Developed Runoff Coefficient (Cd) 0.87
Time of Concentration (min) 8.0
Clear Peak Flow Rate (cfs) 7.4679
Burned Peak Flow Rate (cfs) 7.4679
24-Hr Clear Runoff Volume (ac-ft) 1.1799
24-Hr Clear Runoff Volume (cu-ft) 51395.2328
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/P1-Q50.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID P1
Area (ac) 2.62
Flow Path Length (ft) 660.89
Flow Path Slope (vft/hft) 0.0087
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 50-yr
Fire Factor 0
LID False
Output Results
Modeled (50-yr) Rainfall Depth (in) 7.8
Peak Intensity (in/hr) 3.973
Undeveloped Runoff Coefficient (Cu) 0.7436
Developed Runoff Coefficient (Cd) 0.8781
Time of Concentration (min) 7.0
Clear Peak Flow Rate (cfs) 9.1404
Burned Peak Flow Rate (cfs) 9.1404
24-Hr Clear Runoff Volume (ac-ft) 1.3461
24-Hr Clear Runoff Volume (cu-ft) 58637.0772
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/P1-Q100.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID P1
Area (ac) 2.62
Flow Path Length (ft) 660.89
Flow Path Slope (vft/hft) 0.0087
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 100-yr
Fire Factor 0
LID False
Output Results
Modeled (100-yr) Rainfall Depth (in) 8.7516
Peak Intensity (in/hr) 4.4577
Undeveloped Runoff Coefficient (Cu) 0.7714
Developed Runoff Coefficient (Cd) 0.882
Time of Concentration (min) 7.0
Clear Peak Flow Rate (cfs) 10.3011
Burned Peak Flow Rate (cfs) 10.3011
24-Hr Clear Runoff Volume (ac-ft) 1.5129
24-Hr Clear Runoff Volume (cu-ft) 65900.3861
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/P2-Q25.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID P2
Area (ac) 1.08
Flow Path Length (ft) 285.53
Flow Path Slope (vft/hft) 0.016
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 25-yr
Fire Factor 0
LID False
Output Results
Modeled (25-yr) Rainfall Depth (in) 6.8484
Peak Intensity (in/hr) 4.0859
Undeveloped Runoff Coefficient (Cu) 0.7507
Developed Runoff Coefficient (Cd) 0.8791
Time of Concentration (min) 5.0
Clear Peak Flow Rate (cfs) 3.8793
Burned Peak Flow Rate (cfs) 3.8793
24-Hr Clear Runoff Volume (ac-ft) 0.4865
24-Hr Clear Runoff Volume (cu-ft) 21189.8241
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/P2-Q50.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID P2
Area (ac) 1.08
Flow Path Length (ft) 285.53
Flow Path Slope (vft/hft) 0.016
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 50-yr
Fire Factor 0
LID False
Output Results
Modeled (50-yr) Rainfall Depth (in) 7.8
Peak Intensity (in/hr) 4.6537
Undeveloped Runoff Coefficient (Cu) 0.7824
Developed Runoff Coefficient (Cd) 0.8835
Time of Concentration (min) 5.0
Clear Peak Flow Rate (cfs) 4.4406
Burned Peak Flow Rate (cfs) 4.4406
24-Hr Clear Runoff Volume (ac-ft) 0.555
24-Hr Clear Runoff Volume (cu-ft) 24173.6632
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/Hydrology/P2-Q100.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID P2
Area (ac) 1.08
Flow Path Length (ft) 285.53
Flow Path Slope (vft/hft) 0.016
50-yr Rainfall Depth (in) 7.8
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 100-yr
Fire Factor 0
LID False
Output Results
Modeled (100-yr) Rainfall Depth (in) 8.7516
Peak Intensity (in/hr) 5.2214
Undeveloped Runoff Coefficient (Cu) 0.8091
Developed Runoff Coefficient (Cd) 0.8873
Time of Concentration (min) 5.0
Clear Peak Flow Rate (cfs) 5.0035
Burned Peak Flow Rate (cfs) 5.0035
24-Hr Clear Runoff Volume (ac-ft) 0.6237
24-Hr Clear Runoff Volume (cu-ft) 27167.8143
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131 Calle Iglesia, Suite 200, San Clemente, CA 92672 (949) 369-6141 www.lgcgeotechnical.com June 26, 2025 Project No. 25041-01
Mr. Matthew J. Waken
Crestfield Townhomes, LLC
27702 Crown Valley Parkway, Suite D-4-197
Ladera Ranch, CA 92694
Subject: Preliminary Geotechnical Evaluati on and Recommendations, Proposed Residential Development, Located at 225 Colorado Pl ace (Motel 6) and 201 Colorado Place, Arcadia, County of Los Angeles, California
In accordance with your request and authorization, LGC Geotechnical, Inc. has performed a preliminary geotechnical evaluation for the proposed residential development, located at 225 Colorado Place (Motel 6) and 201 Colorado Place in the City of Arcadia, County of Los Angeles, California. The purpose of our study was to evaluate the existing onsite geotec hnical conditions and to provide geotechnical recommendations relative to the proposed residential development.
Should you have any questions regarding this report, please do not hesitate to contact our office. We appreciate this opportunity to be of service.
Respectfully Submitted,
LGC Geotechnical, Inc.
Ryan Douglas, PE, GE 3147 Mason Gonzales, PG 10174
Vice President of Engineering Project Geologist
John Navarrete
Senior Staff Engineer
RLD/JMN/amm
Distribution: (1) Addressee (electronic copy)
Project No. 25041-01 Page i June 26, 2025
TABLE OF CONTENTS
Section Page
1.0 INTRODUCTION ...................................................................................................................................... 1
1.1 Purpose and Scope of Services ............................................................................................. .............. 1
1.2 Project Description ....................................................................................................... .......................... 1
1.3 Subsurface Geotec hnical Evaluation ........................................................................................ ....... 3
1.4 Field Infiltration Testing ................................................................................................ ...................... 3
1.5 Laboratory Testing ........................................................................................................ ......................... 4
2.0 GEOTECHNICAL CONDITIONS ............................................................................................................. 6
2.1 Regional Geology .......................................................................................................... ........................... 6
2.2 Site-Specific Geology and Generalized Subsurface Conditions ............................................... 6
2.3 Groundwater ............................................................................................................... .............................. 7
2.4 Seismic Desi gn Criteria ................................................................................................... ...................... 7
2.5 Faulting .................................................................................................................. ..................................... 8
2.5.1 Liquefaction and Dynamic Settlement .............................................................................. 9
2.5.2 Lateral Spreading ....................................................................................................... ............. 10
2.6 Oversized Material ........................................................................................................ ........................ 10
2.7 Expansion Potential ....................................................................................................... ....................... 10
3.0 CONCLUSIONS ........................................................................................................................................ 11
4.0 PRELIMINARY RECOMMENDATIONS ............................................................................................ 12
4.1 Site Earthwork ............................................................................................................ ........................... 12
4.1.1 Site Preparation ........................................................................................................ ............... 12
4.1.2 Removal and Recompaction Depths and Limits .......................................................... 13
4.1.3 Temporary Excavations ................................................................................................... .... 14
4.1.4 Removal Bottoms and Subgrade Preparation .............................................................. 15
4.1.5 Material for Fill ....................................................................................................... ................. 15
4.1.6 Placement and Compaction of Fills ................................................................................... 16
4.1.7 Trench and Retaining Wall Backfill and Compaction ................................................. 16
4.1.8 Shrinkage an d Subsidence ................................................................................................ .. 17
4.2 Preliminary Foundation Recommendations ............................................................................... 18
4.2.1 Provisional Conventional Foun dation Design Parameters .................................... 18
4.2.2 Provisional Post-Tensioned Fo undation Design Parameters ............................... 18
4.2.3 Post-Tensioned Foundation Subgra de Preparation and Maintenance ............. 18
4.2.4 Slab Underlayme nt Guidelines .......................................................................................... 19
4.3 Soil Bearing and Lateral Resistance ....................................................................................... ....... 20
4.4 Lateral Earth Pressure s for Retaining Walls .............................................................................. 20
4.5 Control of Surface Water and Drainage Control ......................................................................... 22
4.6 Subsurface Water Infiltration ............................................................................................. .............. 23
4.7 Preliminary Asphal t Pavement Sections .................................................................................... 25
4.8 Soil Corrosivity .......................................................................................................... ............................. 26
4.9 Nonstructural Concrete Flatwork ........................................................................................... ........ 27
4.10 Geotechnical Plan Review ................................................................................................. ................. 28 TABLE OF CONTENTS (Cont’d)
Project No. 25041-01 Page ii June 26, 2025
4.11 Geotechnical Observation and Testing During Construction ................................................ 28
5.0 LIMITATIONS ......................................................................................................................................... 29
LIST OF ILLUSTRATIONS, TABLES, AND APPENDICES
Figures
Figure 1 – Site Location Map (Page 2)
Figure 2 – Boring Location Map (Rear of Text)
Figure 3 – Retaining Wall Backfill Detail (Rear of Text)
Tables
Table 1 – Summary of Field Infiltration Testing (Page 4) Table 2 – Seismic Design Parameters (Page 8)
Table 3 – Lateral Earth Pressures – Approved Onsite or Imported Sandy Soils (Page 21) Table 4 – Shallow Surface Infiltration - Reduction Factors Applied to Infiltration Rate (Page 24)
Table 5 – Preliminary Pavement Sections (Page 25)
Table 6 – Nonstructural Concrete Flatwork Guidelines for Very Low Expansion Potential (Page 27)
Appendices
Appendix A – References
Appendix B – Boring Logs
Appendix C – Laboratory Test Results
Appendix D – Infiltration Test Results
Appendix E – General Earthwork and Grading Specifications for Rough Grading
Project No. 25041-01 Page 1 June 26, 2025
1.0 INTRODUCTION
1.1 Purpose and Scope of Services
This report presents the results of our prelim inary geotechnical evaluation for the proposed residential development, located at 225 and 201 Colorado Place in the City of Arcadia, County of Los Angeles, California. Refer to the Site Location Map (Figure 1).
The purpose of our study was to provide a geotechnical evaluation relative to the proposed residential development. As part of our scope of work, we have: 1) reviewed available geotechnical information and in-house geologic maps pertinent to the site (Appendix A); 2) performed a subsurface geotechnical evaluation of the site consisting of the excavation and sampling of eight small-diameter borings ranging from approximately 10.0 to 50.5 feet below existing ground surface, 3) performed four fallin g head infiltration tests within the borings; 4) performed laboratory testing of select soil samples obtained du ring our subsurface evaluation; and 5) prepared this preliminary geotechnical summary report presenting our findings and preliminary conclusions and recommendations for the development of the proposed project.
It should be noted that our evaluation and this report only address geotechnical issues associated with the site and do not address any environmental issues.
1.2 Project Description
The approximately 3.7-acre site is bound to the north by Barnhart School and west by Colorado P l a c e , t o t h e e a s t b y e x i s t i n g r e s i d e n t i a l h o m e s an d t o t h e s o u t h b y S a n J u a n D r i v e . T h e s i t e i s currently occupied by a Motel 6 on the nort hern portion and the California Thoroughbred Breeders Association building on the southern portion.
The site is bisected by an open U-shaped channel (wash) which runs north to south along the east side of the Motel 6 parcel leading into an underground culvert that spits the Motel 6 parcel and Thoroughbred parcel in the southern portion of the overall site. The exact dimensions and details of the channel and culvert are unknown at this time and the agency that owns the channel and culvert may have specific guidelines for lo ading and setback from the improvements. The proposed improvements relative to the existing channel and culvert should be further reviewed when grading plans are further developed and the details regarding the channel/culvert are available for review.
The proposed development consists of 86 multi-fa mily residential units, internal drive alleys, open space and other associated improvements. Design cut and fill information is not available at this time but is expected to be on the order of less than 2 to 3 feet. The proposed residential development is anticipated to consist of relatively light building loads (column and wall loads maximum of 20 kips and 2 kips per linear foot, respectively).
The recommendations given in this report are based upon at-grade structures with estimated structural loads and grading information indicated above. LGC Geotechnical should be provided with any updated project information, plans and/or any structural loads when they become available, in order to either confirm or modify the recommendations provided herein. 6LWH/RFDWLRQ
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Project No. 25041-01 Page 3 June 26, 2025
1.3 Subsurface Geotechnical Evaluation
A limited subsurface geotechnical evaluation of the site was performed by LGC Geotechnical. Our exploration program consisted of drilling and sampling eight small-diameter exploratory hollow- stem borings (HS-1 through HS-4 and I-1 through I-4) for the purpose of obtaining samples for evaluation and laboratory testing of site soils and performing infiltration testing.
The borings were drilled by Choice Drilling under subcontract to LGC Geotechnical. The depths of the borings ranged from approximately 10.0 to 50.5 feet below existing grade. An LGC Geotechnical representative observed the drilling operations, lo gged the borings, and collected soil samples for laboratory testing. The borings were performed using a truck-mounted drill rig equipped with 8-inch-diameter hollow-stem augers. Bulk samples of the near-surface soils were logged and collected for laboratory testing from select borings. Driven soil samples were collected by means of the Standard Penetration Test (SPT) and Modified California Drive (MCD) sampler generally obtained at 2.5 and 5-foot ve rtical increments. The MCD is a split-barrel sampler with a tapered cutting tip and lined with a s e r i e s o f 1 - i n c h - t all brass rings. The SPT sampler (1.4-inch ID) and MCD sampler (2.4-inch ID, 3.0-inch OD) were driven using a 140- pound automatic hammer falling 30 inches to advance the sampler a total depth of 18 inches or until refusal. The raw blow counts for each 6-inch increment of penetration were recorded on the boring logs. The borings were subsequently backfilled with soil cuttings and tamped and capped with asphalt cold patch. Some settlement of the backfill soils may occur over time.
Infiltration testing was performed within the four borings (I-1 through I-4) to depths of approximately 10 to 15 feet below existing gr ade. An LGC Geotechnical engineer installed standpipes, backfilled the borings with crushed rock and pre-soaked the infiltration holes prior to testing. Infiltration testing was performed per the County of Los Angeles testing guidelines (2021). Standpipes were removed and the location s were subsequently backfilled with native soils at the completion of testing. Some settlement of the backfill soils may occur over time.
The approximate locations of our subsurface expl orations are provided on the Boring Location Map (Figure 2). The boring logs are provided in Appendix B.
1.4 Field Infiltration Testing
Four shallow infiltration test wells were inst alled in Borings I-1 through I-4 to approximate depths of 10 to 15 feet below existing grade. Th e approximate infiltration boring locations are shown on the Boring Location Map (Figure 2). Estimation of infiltration rates was performed in general accordance with the “Boring Percolation Test Procedure” guidelines set forth by the County of Los Angeles testing guidelines (2021). The borings for the infiltration tests were excavated using a drill rig equipped with 8-in ch diameter hollow-stem augers. A 3-inch diameter perforated PVC pipe was placed in the borehole above a thin layer of gravel and the annulus was backfilled wi th gravel. Infiltration tests were performed using relatively clean water free of particulates, silt, etc. The infiltration wells were pre-soaked during the day of drilling and a 30-minute pre-test was performe d during the day of testing. Subsequently, readings were taken a minimum of 6 times or until a “stabilized rate” was established. A “stabilized rate” is when the highest and lowest readings are within 10 percent of each other over three consecutive readings. At the completion of infiltration testing, the pipe was removed, and the holes were backfilled and tamped.
Project No. 25041-01 Page 4 June 26, 2025
Based on the County of Los Angeles testing guidelines (2021), the infiltration rate is calculated by dividing the volume of water discharged by the surface area of the test section (including the sidewalls and bottom of the boring) over a specific time period. The infiltration rate is taken as the average of the last three readings during which a “stabilized rate” is achieved. The infiltration rates are provided in Table 1 below.
TABLE 1
Summary of Field Infiltration Testing
Infiltration Test
Location
Approximate
Infiltration Test
Depth (ft)
Infiltration Rate*
(inch/hr.)
I-1 10.0 0.7
I-2 15.0 6.9
I-3 15.0 5.3
I-4 10.0 4.4
*Does Not Include Required Reduction Factors for Design.
Please note that the values provided in Table 1 do not include reduction factors associated with the test procedure, site variability, and long-ter m siltation plugging that are used to calculate the design infiltration rate. Infiltration test data is presented in Appendix D. Refer to Section 4.6 for recommendations regarding infiltration of stormwater.
1.5 Laboratory Testing
Representative bulk, grab, and driven (relatively undisturbed) samples were retained for laboratory testing during our field evaluation. Laboratory testing included in-situ moisture content and in-situ dry density, expansion index, fines content, Atterberg limits, consolidation, direct shear, laboratory compaction, and corrosion (sulfate, chloride, pH and minimum resistivity).
The following is a summary of the laboratory test results:
x Dry density of the samples collected ranged from approximately 99 pounds per cubic foot (pcf) to 119 pcf, with an average of 110 pcf. Field moisture contents ranged from approximately 2 to 14 percent, with an average of approximately 7 percent. x Two Expansion Index (EI) tests was performed. The results indicate an EI value of 1, corresponding to “Very Low” expansion potential.
x Three samples were tested for fines content indicating a fines content (passing No. 200 sieve) ranging from 4 to 38 percent. Accordin g to the Unified Soils Classification System (USCS), the tested samples are classified as “coarse grained” soil. x Two Atterberg Limit (liquid limit and plastic li mit) test was performed. Results indicated a Plasticity Index (PI) range of 4 to 7.
x Two consolidation tests were performed. The deformation versus vertical stress plots are provided in Appendix C.
Project No. 25041-01 Page 5 June 26, 2025
x Two direct shear test was performed. The plots are provided in Appendix C. x Laboratory compaction of a near-surface bulk sample resulted in a maximum dry density of 130.5 pcf at an optimum moisture content of 8.5 percent. x Corrosion testing indicated soluble sulfate cont ent of less than 0.01 percent, a chloride content ranging from 28 to 29 parts per million (ppm), pH ranging from 7.4 to 7.6 and a minimum resistivity ranging from 13,400 to 15,410 ohm-centimeters.
A summary of the laboratory test results is presented in Appendix C. The moisture and dry density results are presented on the boring logs in Appendix B.
Project No. 25041-01 Page 6 June 26, 2025
2.0 GEOTECHNICAL CONDITIONS
2.1 Regional Geology
The site is located south of the foothills belo w the San Gabriel Mountains in the northern San Gabriel Valley within the transition area of Ca lifornia’s Peninsular and Transverse geomorphic provinces. The Peninsular Ranges are characterized by northwest trending mountain ranges, generally dominated by right lateral strike-slip faulting. The Transverse Ranges are characterized by predominately east-west trending mountain ranges dominated by reverse faulting. The Transverse Ranges geomorphology can be generally be attributed to the effects of the major bend within the northwest trending San Andreas faul t and the subsequent north-south compression that results. The San Gabriel Mountain Range rises steeply north of the site and provides the sediment source for the alluvial fan deposits that underlie the area of the subject site (CGS, 2018).
The site is within the San Gabriel Valley, west of the Santa Anita Wash (Dibblee, et al, 1998).
The subject area is more locally geologically bounded at the north by the Raymond Fault (approximately 700 feet north of the site) and the Sierra Madre Fault Zone (approximately 2 miles north of the site). The Sierra Madre Fault Zone consists of reverse faults dipping to the north. The northeast trending Raymond Fault joins the east west trending Sierra Madre Fault Zone approximately 3 miles to the northeast of the site. The Raymond Fault is a left lateral fault that is generally assumed to be a part of the San Andreas Fault system.
2.2 Site-Specific Geology and Generalized Subsurface Conditions
Based on review of the available geologic map (Dibblee, et al, 1998), the primary geologic unit underlying the site is Quaternary alluvial depo sits. The undissected fan is largely described as alluvial gravel, sand, and silt (Dibblee, et al, 1998).
The field explorations (borings) indicate the nati ve alluvial soils generally consist of variable amounts of clayey sand, silty sand, and sand ra nging from brown to gray, dry to moist, and generally medium dense/medium stiff to very dense/very stiff to the maximum explored depth o f a p p r o x i m a t e l y 5 0 . 5 f e e t b e l o w e x i s t i n g g r a d e . P o t e n t i a l l y u p t o f i v e f e e t o f u n d o c u m e n t e d artificial fill may be present across the site but was not differentiated on the boring logs. Deeper amounts of undocumented fill, not encountered in the borings, may exist locally beneath the current building footprints and in various other areas across the site. These materials should be removed to competent native materials prior to placement of compacted fill.
It should be noted that borings are only representative of the location and time where/when they are performed and varying subsurface conditions may exist outside of the performed location. In addition, subsurface conditions can change over time. The soil descriptions provided above should not be construed to mean that the subs urface profile is uniform, and that soil is homogeneous within the project area. For details on the stratigraphy at the exploration locations, refer to Appendix B.
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2.3 Groundwater
Groundwater was not encountered to the maxi mum depth of approximately 50.5 feet below existing ground surface during our subsurface ev aluation. Historic high groundwater is greater than 100 feet below current grade per the Seis m i c H a z a r d R e p o r t o f t h e M o u n t W i l s o n 7 . 5 - Minute Quadrangle, (CDMG, 1998). Groundwater is not expected to impact the proposed development.
Seasonal fluctuations of groundwater elevations should be expected over time. In general, groundwater levels fluctuate with the seasons and local zones of perched groundwater may be present due to local seepage caused by irrigati on and/or recent precipitation. Local perched groundwater conditions or surface seepage may develop once site development is completed.
2.4 Seismic Design Criteria
The site seismic characteristics were evaluated per the guidelines set forth in Chapter 16, Section 1613 of the 2022 California Building Code (CBC) and applicable portions of ASCE 7-16 which has been adopted by the CBC. Please note that the following seismic parameters are only applicable for code-based acceleration response spectra and are not applicable for where site-specific ground motion procedures are required by ASCE 7-16. Representative site coordinates of latitu de 34.143305 degrees north and lo ngitude -118.039915 degrees west were utilized in our analyses. The maximum co nsidered earthquake (MCE) spectral response accelerations (SMS and SM1) and adjusted design spectral response acceleration parameters (S DS and SD1) for Site Class D are provided in Table 2 on the following page. Since site soils are Site Class D, additional adjustments are required to code acceleration response spectrums as outlined below and provided in ASCE 7-16. The structural designer should contact the geotechnical consultant if structural conditions (e.g., number of stories, seismically isolated structures, etc.) require site-specific ground motions.
A deaggregation of the PGA based on a 2,475-year average return period (MCE) indicates that an earthquake magnitude of 7.05 at a distance of 8.76 km from the site would contribute the most to this ground motion. A deaggregation of the PGA based on a 475-year average return period (Design Earthquake) indicates that an earthquake magnitude of 6.96 at a distance of
13.79 km from the site would contribute the most to this ground motion (USGS, 2014).
Section 1803.5.12 of the 2022 CBC (per Section 11.8.3 of ASCE 7) states that the maximum considered earthquake geometric mean (MCE G) Peak Ground Acceleration (PGA) should be used for liquefaction potential. The PGA M for the site is equal to 0.958g (SEAOC, 2025). The design PGA is equal to 0.639g (2/3 of PGAM).
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TABLE 2
Seismic Design Parameters
Selected Parameters from 2022 CBC,
Section 1613 - Earthquake Loads
Seismic
Design
Values
Notes/Exceptions
Distance to applicable faults classifies the site as a
“Near-Fault” site. Section 11.4.1 of ASCE 7
Site Class D* Chapter 20 of ASCE 7
Ss (Risk-Targeted Spectral Acceleration
for Short Periods) 2.000g From SEAOC, 2025
S1 (Risk-Targeted Spectral
Accelerations for 1-Second Periods) 0.736g From SEAOC, 2025 Fa (per Table 1613.2.3(1)) 1.000
For Simplified Design Procedure
of Section 12.14 of ASCE 7, Fa
shall be taken as 1.4 (Section
12.14.8.1)
Fv (per Table 1613.2.3(2)) 1.700
Value is only applicable per
requirements/exceptions per
Section 11.4.8 of ASCE 7
SMS for Site Class D
[Note: SMS = FaSS] 2.000g -
SM1 for Site Class D
[Note: SM1 = FvS1] 1.251g
Value is only applicable per
requirements/exceptions per
Section 11.4.8 of ASCE 7
SDS for Site Class D
[Note: SDS = (2/3)SMS] 1.333g -
SD1 for Site Class D
[Note: SD1 = (2/3)SM1] 0.834g
Value is only applicable per
requirements/exceptions per
Section 11.4.8 of ASCE 7
CRS (Mapped Risk Coefficient at 0.2 sec) 0.888 ASCE 7 Chapter 22 CR1 (Mapped Risk Coefficient at 1 sec) 0.891 ASCE 7 Chapter 22 *Since site soils are Site Class D and S 1 is greater than or equal to 0.2, the seismic response coefficient Cs is determined by Eq. 12.8-2 for value ζ ͳ Ǥ ͷ s and taken equal to 1.5 times the value calculated in accordance with either Eq. 12.8-3 for T L ηεs, or Eq. 12.8-4 εL. Refer to ASCE 7-16.
2.5 Faulting
P r o m p t e d b y d a m a g i n g e a r t h q u a k e s i n N o r t h e r n and Southern California, State legislation and policies concerning the classification and land-u se criteria associated with faults have been developed. Their purpose was to prevent the co nstruction of urban developments across the t r a c e o f a c t i v e f a u l t s , r e s u l t i n g i n t h e A l q u i s t - P r i o l o E a r t h q u a k e F a u l t Z o n i n g A c t . E a r t h q u a k e Fault Zones have been delineated along the traces of active faults within California. Where developments for human occupation are proposed within these zones, the state requires detailed
Project No. 25041-01 Page 9 June 26, 2025
fault evaluations be performed so that engineering geologists can mitigate the hazards associated with active faulting by identifying the location of active faults and allowing for a setback from the zone of previous ground rupture.
T h e s u b j e c t s i t e i s n o t l o c a t e d w i t h i n a S t a t e o f C a l i f o r n i a E a r t h q u a k e F a u l t Z o n e ( A l q u i s t - Priolo) and no active faults are identified on the site (CGS, 2025). The possibility of damage due to ground rupture is considered low since no active faults are known to cross the site.
Secondary effects of seismic shaking resulting from large earthquakes on the major faults in the Southern California region, which may affect the site, include ground lurching and shallow ground rupture, soil liquefaction, and dynamic settlement. These secondary effects of seismic shaking are a possibility throughout the Southern California region and are dependent on the distance between the site and causative fault and the onsite geology. The closest major active faults that could produce these secondary effe cts include the Sierra Madre, Raymond, San Andreas, and Puente Hills Faults, among others. A discussion of these secondary effects is provided in the following sections.
2.5.1 Liquefaction and Dynamic Settlement
Liquefaction is a seismic phen omenon in which loose, saturated, granular soils behave similarly to a fluid when subject to high-intensity ground shaking. Liquefaction occurs when three general conditions coexist: 1) shallow groundwater; 2) low density non- cohesive (granular) soils; and 3) high-intensity ground motion. Studies indicate that saturated, loose near-surface cohesionless soils exhibit the highest liquefaction potential, while dry, dense, cohesionless soils and cohesive soils exhibit low to negligible liquefaction potential. In general, cohesi ve soils are not considered susceptible to liquefaction, depending on their plasticity and moisture content (Bray & Sancio, 2006).
Effects of liquefaction on level ground include settlement, sand boils, and bearing capacity failures below structures. Dynamic settlement of dry loose sands can occur as the sand particles tend to settle and densify as a result of a seismic event.
Based on our review of the State of California Department of Conservation, Earthquake Zones of Required Investigation (CGS, 2025), the subject site is not within a liquefaction hazard zone. Based on our evaluation, site soils are generally not susceptible to liquefaction due to the lack of a static groundwater table within the upper 50 feet and relatively dense on-site soils. However isolat ed sand layers may be susceptible to dry sand seismic settlement. Seismically induce d dry sand settlement s were estimated by the procedures outlined by Pradel (Pradel, 1998) and utilizing the design earthquake parameters. Based on the data obtained from our field evaluation, seismic settlement due to dry sands is estimated to be on the order of about 0.5-inches. Differential seismic settlement may be estimated as one-half of the total settlement over a horizontal span of 40 feet (e.g., 0.25-inch over a horizontal span of 40 feet).
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2.5.2 Lateral Spreading
Lateral spreading is a type of liquefaction-i nduced ground failure associated with the lateral displacement of surficial blocks of sediment resulting from liquefaction in a s u b s u r f a c e l a y e r . O n c e l i q u e f a c t i o n t r a n s f o r m s t h e s u b s u r f a c e l a y e r i n t o a f l u i d m a s s , gravity plus the earthquake inertial forc es may cause the mass to move downslope towards a free face (such as a river channel or an embankment). Lateral spreading may cause large horizontal displacements and su ch movement typically damages pipelines, utilities, bridges, and structures.
D u e t o t h e l a c k o f g r o u n d w a t e r i n t h e u p p e r 5 0 f e e t , a n d v e r y l o w p o t e n t i a l f o r liquefaction, the potential for lateral spreading is considered very low.
2.6 Oversized Material
Oversized materials (material larger than 8 inches in maximum dimension) may be encountered during site grading based on ou r subsurface evaluation. If encountered, recommendations are provided for appropriate handling of oversized materials in Appendix E.
2.7 Expansion Potential
Based on the results of our laboratory testing, site soils are anticipated to have a “Very Low” expansion potential. Final expansion potential of site soils should be determined at the completion of grading. Results of expansion testing at finish grades will be utilized to confirm final foundation design.
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3.0 CONCLUSIONS
Based on the results of our geotechnical evaluation, it is our opinion that the proposed development is feasible from a geotechnical standpoint, provided the following conclusions and recommendations are implemented.
The following is a summary of the primary geotechnic al factors that may affect future development of the site:
x In general, field explorations (borings) indicate primarily native soils consisting of variable amounts of sandy clay, sandy silt, sand, silty sand and clayey sand, which are gray to brown, dry to moist, and generally loose/medium stiff to very dense, to the maximum explored depth of approximately 50.5 feet below existing grade. The near-surface loose and compressible soils are not suitable for the planned improvements in their present condition (refer to Section 4.1). x Groundwater was not encountered during our subs urface evaluation to the maximum explored depth of approximately 50.5 feet below current grad e. Historic high groundwater is greater than 100 feet below current grade (CDMG, 1998).
x T h e s u b j e c t s i t e i s n o t l o c a t e d w i t h i n a s t a t e o f C a l i f o r n i a E a r t h q u a k e F a u l t Z o n e ( C G S , 2 0 2 5 ) . T h e main seismic hazard that may affect the site is ground shaking from one of the active regional faults.
The subject site will likely experience strong seismic ground shaking during its design life. x Based on our review of the State of California Department of Conservation, Earthquake Zones of Required Investigation (CGS, 2025), the subject site is not within a liquefaction hazard zone. The potential for liquefaction is considered very low due to the lack of groundwater in the upper 50 feet and very dense on-site soils. However, isolated sand layers may be susceptible to dry sand seismic settlement. Total seismic settlement is estimated to be on the order 0.5-inch. Differential seismic settlement may be estimated as one-half of the total seismic settlement over a horizontal span of 40 feet.
x Based on the results of preliminary laboratory testing, site soils are anticipated to have “Very Low” expansion potential. Final design expansion potent ial must be determined at the completion of grading.
x Some of the onsite soils may not be suitable for retaining wall backfill due to the fines content; therefore, select grading and stockpiling of the onsite sandy soils or import of sandy soils meeting the project requirements should be anticipated by the contractor. x Excavations into the existing site soils should be feasible with heavy construction equipment in good working order. From a geotechnical perspective, the existing onsite soils are suitable material for use as fill, provided that they ar e relatively free from oversized material (larger than 8 inches in maximum dimension), construction debris, and significant organic material. x Oversized material (material larger than 8 inch es in maximum dimension) may be encountered during site grading based on our subsurface evaluation.
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4.0 PRELIMINARY RECOMMENDATIONS
The following recommendations are to be consider ed preliminary and should be confirmed upon completion of grading and earthwork operations. In addition, they should be considered minimal from a geotechnical viewpoint, as there may be more rest rictive requirements from the architect, structural engineer, building codes, governing agencies, or the owner.
It should be noted that the following geotechnical recommendations are intended to provide sufficient information to develop the site in general accordance with the 2022 CBC requirements. With regard to the potential occurrence of potent ially catastrophic geotechnical hazards such as fault rupture, earthquake-induced landslides, liqu efaction, etc. the following geot echnical recommendations should provide adequate protection for the proposed develo pment to the extent required to reduce seismic risk to an “acceptable level.” The “acceptable level” of risk is de fined by the California Code of Regulations as “that level that provides reasonable protection of the public safety, though it does not necessarily ensure continued structural integrity and functionality of the project” [Section 3721(a)].
Therefore, repair and remedial work of the pr oposed improvements may be required after a significant seismic event. With regards to the potential for less significant geologic hazards to the proposed development, the recommendations cont ained herein are intended as a reasonable protection against the potential damaging effects of geotechnical phenomena such as expansive soils, fill settlement, groundwater seepage, etc. It should be understood, however, that although our recommendations are intended to maintain the stru ctural integrity of the proposed development and structures given the site geotechnical conditions, they cannot preclude the potential for some cosmetic distress or nuisance issues to develop as a result of the site geotechnical conditions.
The geotechnical recommendations contained herein must be confirmed to be suitable or modified based on the actual as-graded conditions.
4.1 Site Earthwork
We anticipate that earthwork at the site will consist of the removal of existing improvements associated with the former land use followed by the required earthw ork removals, precise grading, and construction of the proposed new improvemen ts, including the residential structures, subsurface utilities, interior drive alleys, etc.
W e r e c o m m e n d t h a t e a r t h w o r k o n s i t e b e p e r f o r m e d i n a c c o r d a n c e w i t h t h e f o l l o w i n g recommendations, future grading plan review report(s), the 2022 CBC/City of Arcadia grading requirements, and the General Earthwork and Grading Specifications included in Appendix E. In case of conflict, the following recommendations shall supersede those incl uded in Appendix E.
The following recommendations should be consid ered preliminary and may be revised within the future grading plan review report or based on the actual conditions encountered during site grading.
4.1.1 Site Preparation
Prior to grading of areas to receive structural fill or engineered improvements, the areas should be cleared of existing asphalt, surface obstructions, and demolition debris.
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Vegetation and debris should be removed and properly disposed of off-site. Holes resulting from the removal of buried obstructions, which extend below proposed finish grades, should be replaced with suitable compacted fill material. Any abandoned sewer or storm drain lines should be completely removed and replaced with properly placed compacted fill. Deeper demolition may be required in order to remove existing foundations. We recommend the trenches as sociated with demolition which extend below the remedial grading depth be backfilled and properly compacted prior to the demolition contractor leaving the site.
If cesspools or septic systems are encountered, they should be removed in their entirety.
The resulting excavation should be backfilled with properly compacted fill soils. As an alternative, cesspools can be backfilled with lean sand-cement slurry. Any encountered wells should be properly abandoned in accordance with regulatory requirements. At the conclusion of the clearing operations, a representative of LGC Geotechnical should observe and accept the site prior to further grading.
4.1.2 Removal and Recompaction Depths and Limits
In order to provide a relatively uniform bearing condition for the planned building structures, upper loose/compressible soils are to be temporarily removed and recompacted as properly compacted fills. Existing undocumented artificial fill within the i n f l u e n c e o f t h e p r o p o s e d s t r u c t u r a l i m p r o v e m e n t s s h o u l d b e r e m o v e d t o s u i t a b l e , competent native materials prior to placement of artificial fill to design grades. For preliminary planning purposes, the depth of required removals and recompaction may be estimated as indicated below. It should be noted that updated recommendations may be required based on changes to building layouts and/or grading plan.
Buildings: Soils shall be temporarily removed and recompacted to a depth ranging from 5 to 6 feet below existing grade or 3 feet be low the bottom of foundations, whichever is deeper. Refer to the Boring Location Map (Figure 2) for recommended remedial grading depths. Where space is available, the enve lope for removal and recompaction should extend laterally a minimum distance equal to the depth of removal and recompaction below finish grade or 5 feet beyond the ed ges of the proposed building improvements, whichever is larger.
Minor Site Structures: For minor site structur es such as free-standing walls, retaining walls, etc., temporary removal and recompacti on should extend a minimum of 3 feet below existing grade or 2 feet below propos ed footings, whichever is greater. Where space is available, the envelope for removal and recompaction should extend laterally a minimum distance of 3 feet beyond the ed ges of the proposed minor site structure improvements.
Pavement and Hardscape Areas: Within pa vement and hardscape areas, temporary removal and recompaction should extend to a depth of at least 2 feet below existing grade or 2 feet below the bottom of the pavement section, whichever is deeper. Pavement areas encountering undocumented fill materials may require deeper removal and recompaction and should be determined based on the conditions exposed during grading. In general, the envelope for removal and recompaction should extend laterally a minimum lateral
Project No. 25041-01 Page 14 June 26, 2025
distance of 2 feet beyond the edges of the proposed pave ment or hardscape improvements.
Local conditions may be encountered during excavation that could require additional over-excavation beyond the above noted mini mum in order to obtain an acceptable subgrade. The actual depths and lateral extents of grading will be determined by the geotechnical consultant, based on subsurface conditions encountered during grading.
Removal areas and areas to be over-excavated should be accurately staked in the field by the Project Surveyor.
4.1.3 Temporary Excavations
Temporary excavations should be performe d in accordance with project plans, specifications, and all Occupational Safe ty and Health Administration (OSHA) r e q u i r e m e n t s . E x c a v a t i o n s s h o u l d b e l a i d b a c k o r s h o r e d i n a c c o r d a n c e w i t h O S H A requirements before personnel or equipment are allowed to enter.
Based on our field evaluation, site soils within the upper 5 to 10 feet are anticipated to be OSHA Type “B” soils (refer to the attached boring logs). Sandy soils are present and should be considered susceptible to caving. Soil conditions should be regularly evaluated during construction to verify conditions are as anticipated. The contractor shall be responsible for providing the “competent pe rson,” required by OSHA standards, to evaluate soil conditions. Clos e coordination with the geotec hnical consultant should be maintained to facilitate construction while providing safe excavations. Excavation safety is the sole responsibility of the contractor.
Where proposed improvements will be adjace nt to property lines, the potential for impacting existing offsite improvements may be reduced by performing “ABC” slot cuts while performing earthwork removal and recompaction. “ABC” slot cuts are defined as excavations perpendicular to sensitive property boundaries that are divided into multiple “slots” of equal width. If slots are labeled A, B, C, A, B, C, etc., then all “A” slots can be excavated at the same time but must be backfilled before all “B” slots can be excavated, etc. Any given slot should be backfilled immediately with properly compacted fill to finish grade prior to excavation of the adjacent two slots. Please note sands susceptible to caving are present at the si te. Recommendations for slot cut dimensions should be evaluated during grading. Protec tion of the existing offsite improvements during grading is the responsibility of the contractor.
Vehicular traffic, stockpiles, and equipment storage should be set back from the perimeter of excavations a distance equivalent to a 1:1 projection from the bottom of the excavation.
O n c e a n e x c a v a t i o n h a s b e e n i n i t i a t e d , i t s h o u l d b e b a c k f i l l e d a s s o o n a s p r a c t i c a l .
Prolonged exposure of temporary excavations may result in some localized instability.
Excavations should be planned so that they are not initiated without sufficient time to shore/fill them prior to weekends, holidays, or forecasted rain.
It should be noted that any excavation that extends below a 1:1 (horizontal to vertical) p r o j e c t i o n o f a n e x i s t i n g f o u n d a t i o n w i l l r e m o v e e x i s t i n g s u p p o r t o f t h e s t r u c t u r e foundation. If requested, temporary shoring parameter will be provided.
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4.1.4 Removal Bottoms and Subgrade Preparation
In general, removal bottom areas and any ar eas to receive compacted fill should be scarified to a minimum depth of 6 inches, brought to near-optimum moisture content (generally within optimum and 2 percent above optimum moisture content), and re- compacted per project recommendations.
Removal bottoms, over-excavation bottoms and areas to receive fill should be observed and accepted by the geotechnical consultant prior to subsequent fill placement. Soil subgrade for planned footings and improvements (e.g., slabs, etc.) should be firm and competent.
4.1.5 Material for Fill
From a geotechnical perspective, the onsite soils are generally considered suitable for use as general compacted fill, provided they are screened of or ganic materials, construction debris, and oversized material (8 inches in greatest dimension).
From a geotechnical viewpoint, any required import soils for general fill (i.e., non- retaining wall backfill) should consist of clea n, granular soils of “Very Low” expansion potential (expansion index 20 or less based on ASTM D 4829), and generally free of organic materials, construction debris and material greater than 3 inches in maximum dimension. Import for required retaining wall backfill should meet the criteria outlined in t h e f o l l o w i n g p a r a g r a p h . S o u r c e s a m p l e s s h o u l d b e p r o v i d e d t o t h e g e o t e c h n i c a l consultant for laboratory testing a minimu m of four working days prior to planned importation.
Retaining wall backfill should consist of sandy soils with a maximum of 35 percent fines (passing the No. 200 sieve) per American Society for Testing and Materials (ASTM) Test Method D1140 (or ASTM D6913/D422) and a “Very Low” expansion potential (EI of 20 or less per ASTM D4829). Soils should also be screened of organic materials, construction debris, and any material greater than 3 inches in maximum dimension. Some of the onsite soils may not be suitable for retaining wall backfill due to fines content; therefore, select grading and stockpiling of the onsite sandy soils or import of sandy soils meeting the criteria outlined above should be anticipate d by the contractor for obtaining suitable retaining wall backfill soil.
Aggregate base (crushed aggregate base or crushed miscellaneous base) should conform to the requirements of Section 200-2 of the Standard Specifications for Public Works Construction (“Greenbook”) for untrea ted base materials (except processed miscellaneous base) or Caltrans Class 2 aggregate base.
The placement of demolition materials in compacted fill is acceptable from a geotechnical viewpoint provided the demolition material is broken up into pieces not larger than approximately 2 to 4 inches in maximum dimension, and well blended into fill soils with essentially no resulting voids. Demolition m a t e r i a l p l a c e d i n f i l l s m u s t b e f r e e o f construction debris (wood, brick, etc.) and reinforcing steel. If asphalt concrete fragments will be incorporated into the demolition ma terials, approval from an environmental
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viewpoint may be required and is not the pu rview of the geotechnical consultant. From our previous experience, we recommend that asphalt concrete fragments be limited to fill areas within planned streets, alleys or non-structural areas (i.e., not within building pad areas).
4.1.6 Placement and Compaction of Fills
Material to be placed as fill should be brought to near-optimum moisture content (generally within optimum and 2 percent above optimum moisture content) and recompacted to at least 90 percent relative compaction (per ASTM D1557). Moisture conditioning of site soils will be required in order to achieve adequate compaction. Soils will generally require additional moisture in order to achieve the required compaction.
Drying and/or mixing the very moist soils may also be required prior to reusing the materials in compacted fills.
The optimum lift thickness to produce a uniformly compacted fill will depend on the type and size of compaction equipment used. In general, fill should be placed in uniform lifts not exceeding 8 inches in compacted thickness. Each lift should be thoroughly compacted and accepted prior to subsequent lifts. Generally, placement and compaction of fill should be performed in accordance with local gr ading ordinances and with observation and testing performed by the geotechnical consultant. Oversized material as previously defined should be removed from site fills. During backfill of excavations, the fill should be properly benched into firm and competent soils of temporary backcut slopes as it is placed in lifts.
Aggregate base material should be compacted to at least 95 percent relative compaction a t o r s l i g h t l y a b o v e o p t i m u m m o i s t u r e c o n t e n t p e r A S T M D 1 5 5 7 . S u b g r a d e b e l o w aggregate base should be compacted to at least 90 percent relative compaction per ASTM D1557 at or slightly above optimum moisture content (generally within optimum and 2 percent above optimum moisture content).
I f g a p - g r a d e d ¾ - i n c h r o c k i s u s e d f o r b ackfill (around storm dr ain storage chambers, retaining wall backfill, etc.) it will require co mpaction. Rock shall be placed in thin lifts (typically not exceeding 6 inches) and mech anically compacted with observation by geotechnical consultant. Backfill rock shall meet the requirements of ASTM D2321. Gap- graded rock is required to be entirely wrapped in filter fabric (Mirafi 140N or approved alternative) or at the very minimum to be vertically separated from the trench backfill with filter fabric to prevent the migration of fines into the rock backfill.
4.1.7 Trench and Retaining Wall Backfill and Compaction
The onsite soils will generally be suitable as trench backfill, provided the soils are screened of rocks and other material greate r than 6 inches in diameter, construction debris and organic matter. Trench backfill should be compacted in uniform lifts (generally not exceeding 12 inches in co mpacted thickness) by mechan ical means to at least 90 percent relative compaction (per ASTM Test Method D1557). If trenches are shallow or the use of conventional equipment may result in damage to the utilities, sand having a
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s a n d e q u i v a l e n t ( S E ) o f 3 0 o r g r e a t e r ( p e r C a l i f o r n i a T e s t M e t h o d [ C T M ] 2 1 7 ) m a y b e used to bed and shade the pipes. Sand backfill within the pipe bedding zone may be densified by jetting or flooding and then tamped to ensure adequate compaction. Sand g r a i n s s h o u l d b e f r o m a n a t u r a l s o u r c e w i t h r o u n d e d s h a p e . M a n u f a c t u r e d s a n d f r o m crushed rock or recycled material is not suit able for jetting/flooding as the grains are typically angular in shape and do not densify well enough with these methods.
Manufactured sand can be used as shading material when mechanical compaction efforts are used. Subsequent trench backfill should be compacted in uniform thin lifts by mechanical means to at least a minimum 90 percent relative compaction (per ASTM D1557). If any ¾-inch rock is used for backfill, see Section 4.1.6 for filter fabric requirements.
Retaining wall backfill should consist of onsite or imported select sandy soils as outlined in preceding Section 4.1.5. The limits of select sandy backfill should extend a minimum ½ the height of the retaining wall or the width of the heel (if applicable), whichever is greater, refer to Figure 3. Retaining wall back fill soils should be compacted in relatively uniform thin lifts to at least 90 percent relative compaction (per ASTM D1557). Jetting or flooding of retaining wall backfill materials should not be permitted.
In backfill areas where mechanical compaction of soil backfill is impractical due to space constraints, typically sand-cement slurry may be substituted for compacted backfill. The slurry should contain about one sack of cement per cubic yard. When set, such a mix typically has the consistency of compacted soil. Sand cement slurry placed near the surface within landscape areas should be evaluated for potential impacts on planned improvements.
A representative from LGC Geotechnical should observe, probe, and test the backfill to verify compliance with the project recommendations.
4.1.8 Shrinkage and Subsidence
Allowance in the earthwork volumes budget should be made for an estimated 5 to 20 percent reduction (shrink) in volume of near-surface (upper approximate 5 feet) soils. It should be stressed that these values are on ly estimates and that an actual shrinkage factor would be extremely difficult to pr edetermine. Subsidence, due to earthwork operations, is expected to be on the order of 0.1 feet. These values are estimates only and exclude losses due to removal of vegetation or debris. The effective shrinkage of onsite soils will depend primarily on the type of compaction equipment and method of compaction used onsite by the contractor and accuracy of the topographic survey.
Due to the combined variability in topographi c surveys, inability to precisely model the removals and variability of on-site near-surface conditions, it is our opinion that the site will not balance at the end of grading. If importing/exporting a large volume of soils is not considered feasible or econom ical, we recommend a balance area be designated onsite t h a t c a n f l u c t u a t e u p o r d o w n b a s e d o n t h e a c t u a l v o l u m e o f s o i l . W e r e c o m m e n d a “balance” area that can accommodate on the order of 5 percent (plus or minus) of the total grading volume be considered.
Project No. 25041-01 Page 18 June 26, 2025
4.2 Preliminary Foundation Recommendations
Provided that the remedial grading recommendations provided herein are implemented, the site may be considered suitable for the support of the residential structures using a conventional or post-tensioned foundation system designed to resist the impacts of expansive soils. Site soils are anticipated to be “Very Low” expansion potential (EI of 20 or less per ASTM D4829) and special design considerations from a geotechnical perspective are not required. The structural designer should use their own judgment in the design of the foundation system. Please note that the following foundation recommendations are preliminary and must be confirmed by LGC Geotechnical at the completion of grading.
Preliminary foundation recommendations are provided in the following sections. Recommended soil bearing and estimated settlement due to structural loads are provided in Section 4.3. The foundation should be designed in consideration of the site seismic settlement as outlined in Section 2.5.1.
4.2.1 Provisional Conventional Foundation Design Parameters
Due to the very low expansion potential of the onsite soils, the foundation/structural engineer may design a conventional foundation system that is tied together based upon the anticipated dead and live loads (wind, seismic) that will be imparted by the structure. The recommendations provided in the “Soil Bearing and Lateral Resistance” section may be utilized in the design of a rigid slab-on-grade conventional foundation designed in accordance with Section 1808 of the 2022 C.B.C.
4.2.2 Provisional Post-Tensioned Foundation Design Parameters
The foundation designer may use a modulus of vertical subgrade reaction (k) of 200 pounds per cubic inch (pounds per square inch per inch of deflection). This value is for a 1-foot by 1-foot square loaded area and sh ould be adjusted by the structural designer for the area of the proposed footing using the following formula:
k = 200 x [(B+1)/2B]2
k = modulus of vertical subgrade reaction, pounds per cubic inch (pci) B = foundation width (feet)
The moisture content of near surface fill soils should be kept at optimum moisture content to a minimum depth of 12 inches prior to trenching and concrete placement.
4.2.3 Foundation Subgrade Preparation and Maintenance
The geotechnical parameters provided herein assume that if the areas adjacent to the foundation are planted and irrigated, these areas will be designed with proper drainage and adequately maintained so that ponding, which causes significant moisture changes below the foundation, does not occur. Our recommendations do not account for excessive irrigation and/or incorrect landscape design. Plants should only be provided
Project No. 25041-01 Page 19 June 26, 2025
with sufficient irrigation for life and not overwatered to saturate subgrade soils. Sunken planters placed adjacent to the foundation sh ould either be designed with an efficient drainage system or liners to prevent moisture infiltration below the foundation. Some lifting of the perimeter foundation beam should be expected even with properly constructed planters.
In addition to the factors mentioned above, future owners/property management p e r s o n n e l s h o u l d b e m a d e a w a r e o f t h e p o t e n t i a l n e g a t i v e i n f l u e n c e s o f t r e e s a n d / o r other large vegetation. Roots that extend near the vicinity of foundations can cause distress to foundations. Future owners (and the owner’s landscape architect) should not plant trees/large shrubs closer to the foundations than a distance equal to half the mature height of the tree or 20 feet, whichever is more conservative unless specifically provided with root barriers to prevent root growth below the building foundation.
It is the owner’s responsibility to perfor m periodic maintenance during hot and dry periods to ensure that adequate watering has been provided to keep soil from separating or pulling back from the fo undation. Future owners and property management personnel should be informed and educated regarding the importance of maintaining a constant level of soil-moisture. The owners should be made aware of the potential negative consequences of both excessive watering, as well as allowing potentially expansive soils to become too dry. Expansive soils can undergo shrinkage during drying, and swelling during the rainy winter season, or when irrigation is resumed. This can result in distress to building structures and hardscape improvements. The builder should provide these recommendations to future owners and property management personnel.
4.2.4 Slab Underl ayment Guidelines
The following recommendations are for informational purposes since they are unrelated to the geotechnical performance of the foundation. Some post-construction moisture migration should be expected belo w the foundation; the foundation engineer must assume soil moisture to be present below the slab. The following recommendations may be superseded by the foundation engineer and/or owner.
In general, interior floor slabs with moisture sensitive floor coverings should be underlain by a minimum 10-15 mil thick vapor retarder, which has a water vapor transmission rate (permeance) of less than 0.3 perms, as determined by ASTM E 96, and meets the applicable code requirements (ASTM E 1745).
It is the responsibility of the contractor to ensure that the moisture/vapor retarder systems are properly installed in accordance with the project plans and manufacturer’s specifications, and that the moisture/vapor retarder materials are free of tears and punctures prior to and as a result of concre te placement. Additional moisture reduction and/or prevention measures may be needed, depending on the performance requirements of future interior floor coverings.
The foundation engineer/architect should determine whether the use of a capillary break (sand or gravel layer) in conjunction with the vapor retarder is necessary or
Project No. 25041-01 Page 20 June 26, 2025
required by code. Sand layer thickness and location (above and/or below vapor retarder) should also be determined by the foundation engineer/architect.
4.3 Soil Bearing and Lateral Resistance
Provided our earthwork recommendations are implemented, an allowable soil bearing pressure of 2,000 pounds per square foot (psf) may be used for the design of footings having a minimum width of 12 inches and minimum embedment of 12 inches below lowest adjacent ground surface.
This value may be increased by 300 psf for each additional foot of em bedment and 150 psf for each additional foot of foundation width to a maximum value of 3,000 psf. A post-tensioned mat foundation a minimum of 6 inches below lowest adjacent grade may be designed for an allowable soil bearing pressure of 1,200 psf. These allo wable bearing pressures are applicable for level (ground slope equal to or flatter than 5H:1V) co nditions only. Bearing values indicated are for
loading (i.e., wind or seismic loads).
In utilizing the above-mentioned allowable be aring capacity and pr ovided our earthwork recommendations are implemented, foundation settlement due to structural loads is anticipated to be 1-inch or less. Differential static settlement may be taken as half of the static settlement (i.e., ½-inch over a horizontal span of 40 feet). Recommendations for estimated seismic settlement are provided in Section 2.5.1.
Res is tanc e to late ral loa d s c an be p rov id ed by fric tion ac ting a t the bas e of found ations and by passive earth pressure. For concrete/soil frictional resistance, an allowable coefficient of friction of 0.35 may be assumed with dead-load forces. For slabs constructed over a moisture retarder, the allowable friction coefficient should be prov ided by the manufacturer. An allowable passive lateral earth pressure of 250 psf per foot of depth (or pcf) to a maximum of 2,500 psf may be used for the sides of footings poured against properly compacted fill. Allowable passive pressure may be increased to 340 pcf (maximum of 3,400 psf) for short duration seismic loading. This passive pressure is applicable for level (ground slope equal to or flatter than 5H:1V) conditions.
For a 2:1 (horizontal to vertical) downward sloping condition, a reduced passive lateral earth pressure of 100 pcf to a maximum of 1,000 psf may be used. This allowable passive pressure may be increased to 135 pcf to a maximum of 1,350 psf for short duration seismic loading.
Frictional resistance and passive pressure may be used in combination without reduction. We recommend that the upper foot of passive resistan ce be neglected if finished grade will not be covered with concrete or asphalt. The provided allowable passive pressures are based on a factor of safety of 1.5 and 1.1 for static and seismic loading conditions, respectively.
4.4 Lateral Earth Pressures for Retaining Walls
Lateral earth pressures for approved native sa ndy or import soils meeting indicated project requirements are provided below. Lateral earth pressures are provided as equivalent fluid unit weights, in psf per foot of depth (or pcf). These values do not contain an appreciable factor of safety, so the retaining wall designer should appl y the applicable factors of safety and/or load factors during design. A soil unit weight of 120 pcf may be assumed for calculating the actual weight of soil over the wall footing.
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The following lateral earth pressures are presented in Table 3 below for approved granular soils with a maximum of 35 percent fines (passing the No. 200 sieve per ASTM D-421/422) and a “Very Low” expansion potential (EI of 20 or less per ASTM D4829). Some of the onsite soils may not be suitable for retaining wall backfill due to fines content; therefore, select grading and stockpiling of the onsite soils or import of soil s meeting the criteria outlined above should be anticipated by the contractor for obtaining suitable retaining wall backfill soil. The wall designer should clearly indicate on the retaining wall plans the required select sandy soil backfill criteria.
These preliminary findings should be confirmed during grading.
TABLE 3
Lateral Earth Pressures – Approved Onsite or Imported Sandy Soils
Conditions
Equivalent Fluid Unit
Weight (pcf)
Equivalent Fluid Unit
Weight (pcf)
Level Backfill 2:1 Sloped Backfill
Approved Sandy Soils Approved Sandy Soils
Active 35 55
At-Rest 55 70
If the wall can yield enough to mobilize the full sh ear strength of the soil, it can be designed for “active” pressure. If the wall cannot yield unde r the applied load, the earth pressure will be higher. This would include 90-degree corners of re taining walls. Such walls should be designed for “at-rest.” The equivalent fluid pressure values assume free-draining conditions. If conditions other than those assumed above are anticipated, the equivalent fluid pressure values should be provided on an individual-case basis by the geotechnical engineer.
R e t a i n i n g w a l l s t r u c t u r e s s h o u l d b e p r o v i d e d w i t h a p p r o p r i a t e d r a i n a g e a n d a p p r o p r i a t e l y waterproofed. To reduce, but not eliminate, saturation of near-surface (upper approximate 1- foot) soils in front of the retaining walls, the pe rforated subdrain pipe should be located as low as possible behind the retaining wall. The outlet pipe should be sloped to drain to a suitable o u t l e t . I n g e n e r a l , w e d o n o t r e c o m m e n d r e t a i n i n g w a l l o u t l e t p i p e s b e c o n n e c t e d t o a r e a drains. If subdrains are connected to area drains, special care and information should be provided to homeowners to maintain these drains. Typical retaining wall drainage is illustrated in Figure 3. It should be noted that the recommended subdrain does not provide protection against seepage through the face of the wall and/ or efflorescence. Efflor escence is generally a white crystalline powder (discoloration) that results when water containing soluble salts m i g r a t e s o v e r a p e r i o d o f t i m e t h r o u g h t h e f a c e o f a r e t a i n i n g w a l l a n d e v a p o r a t e s . I f s u c h seepage or efflorescence is undesirable, retainin g walls should be waterp roofed to reduce this potential. Please note that waterproofing an d outlet systems are not the purview of the geotechnical consultant.
Surcharge loading effects from any adjacent stru ctures should be evaluated by the retaining wall designer. In general, structural loads within a 1:1 (horizontal to vertical) upward
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projection from the bottom of the proposed retaining wall foot ing will surcharge the proposed retaining wall. In addition to the recommended earth pressure, retaining walls adjacent to streets should be designed to resist a unifor m lateral pressure of 80 pounds per square foot (psf) due to normal street vehicle traffic if applicable. Uniform lateral surcharges may be estimated using the applicable coefficient of lateral earth pressure using a rectangular distribution. A factor of 0.45 and 0.3 may be used for at-rest and active conditions, respectively.
The retaining wall designer should contact th e geotechnical engineer for any required geotechnical input in estimating any applicable surcharge loads.
If retaining walls greater than 6 feet in height are proposed, the retaining wall designer should contact the geotechnical engineer for specific seismic lateral earth pressure increments based on the configuration of the planned retaining wall structures.
Soil bearing and lateral resistan ce (friction coefficient and passive resistance) are provided in Section 4.3. Earthwork considerations (temporary backcuts, backfill, compaction, etc.) for retaining walls are provided in Section 4.1 (S ite Earthwork) and the subsequent earthwork related sub-sections.
4.5 Control of Surface Water and Drainage Control
From a geotechnical perspective, positive draina ge of surface water away from structures is v e r y i m p o r t a n t . W a t e r s h o u l d n o t b e a l l o w e d t o p o n d a d j a c e n t t o b u i l d i n g s o r t o f l o w f r e e l y down a graded slope. Per section 1804.4 of the 2022 CBC, positive drainage may be accomplished by providing drainage away from bu ildings at a gradient of at least 5 percent for earthen surfaces for a distance of at least 10 feet away from the face of wall. If a distance of 10 feet cannot be achieved, an alternative of a gradie nt of at least 5 percent to an area drain or swale having a gradient of 2 percent is accept able. Where necessary, drainage paths may be shortened by use of area drains and collector pipes. Eave gutters are recommended and should reduce water infiltration into the subgrade soils if the downspouts are properly connected to appropriate outlets. Ultimately surface drainage and code compliance are the purview of the project civil engineer.
Planters with open bottoms adjacent to building s should be avoided. Planters should not be designed adjacent to buildings unless provisions for drainage, such as catch basins, liners, and/or area drains, are made. Overwatering must be avoided.
P l a n t e r s a d j a c e n t t o a b u i l d i n g o r s t r u c t u r e s h o u l d b e a v o i d e d w h e r e v e r p o s s i b l e o r b e properly designed (e.g., lined with a membrane), to reduce the penetration of water into the adjacent footing subgrades and thereby reduce moisture related damage to the foundation.
P l a n t i n g a r e a s a t g r a d e s h o u l d b e p r o v i d e d with appropriate positive drainage. Wherever possible, exposed soil areas should be above ad jacent paved grades to facilitate drainage.
Planters should not be depressed below adjacent paved grades unless provisions for drainage, such as multiple depressed area drains, are cons tructed. Adequate drainage gradients, devices, a n d c u r b i n g s h o u l d b e p r o v i d e d t o p r e v e n t r u n o f f f r o m a d j a c e n t p a v e m e n t o r w a l k s i n t o t h e p l a n t i n g a r e a s . I r r i g a t i o n m e t h o d s s h o u l d p r o m o t e u n i f o r m i t y o f m o i s t u r e i n p l a n t e r s a n d beneath adjacent concrete flatwork. Overwateri ng and underwatering of landscape areas must be avoided.
Project No. 25041-01 Page 23 June 26, 2025
Area drain inlets should be maintained and kept clear of debris in order to properly function.
H o m e o w n e r s s h o u l d a l s o b e m a d e a w a r e t h a t e x c e s s i v e i r r i g a t i o n o f n e i g h b o r i n g p r o p e r t i e s can cause seepage and moisture conditions on ad jacent lots. Homeowners should be furnished with these recommendations communicating the importance of maintaining positive drainage away from structures, towards streets, when they design their improvements.
T h e i m p a c t o f h e a v y i r r i g a t i o n o r i n a d e q u a t e runoff gradients can create perched water conditions. This may result in seepage or shallow groundwater conditions where previously none existed. Maintaining adequate surface drainage and controlled irrigation will significantly reduce the potential for nuisance-type moisture problems. To reduce differential earth movements such as heaving and shrinkage due to the change in moisture content of foundation soils, which may cause distress to a residential structure and associated improvements, moisture content of the soils surrounding the structure should be kept as relatively constant as possible.
Subdrains and v-ditches must be properly maintained, and their outlets kept free draining and clear of any potential obstructions. Routine maintenance should be performed, especially prior to and during the rainy season. Failure to properly maintain these elements may result in slope failures, slumps, excessive erosion, localized saturated zones, nuisance type water issues, etc.
Any future trenches excavated on a slope face for utility or irrigation lines and/or for any purpose should be properly backfilled and compacted to the slope face. Observation/testing and acceptance by the geotechnical consultant during trench backfill are recommended.
A program for the elimination of burrowing animals in both native and graded slope areas must be established and properly maintained to protec t slope stability by reducing the potential for surface water to penetrate into the soil. Cont inuous erosion control, rodent control, and maintenance are essential to the long-term stability of all slopes.
4.6 Subsurface Water Infiltration
It should be noted that intentionally infiltrati ng storm water conflicts with the geotechnical engineering objective of directing surface wate r away from structures and improvements. The geotechnical stability and integrity of a site is reliant upon appropriately handling surface water.
In general, the vast majority of geotechnical distress issues are directly related to improper drainage. Distress in the form of movement of foundations and other improvements could occur as a result of soil saturation and loss of soil support of foundations and pavements, settlement, collapse, internal soil erosion, and/or expansion. Additionally, off-site properties and improvements may be subjected to seepage, spri ngs, instability, movements of foundations or other impacts as a result of water infiltrati on and migration. Infi ltrated water may enter underground utility pipe zones or other highly permeable layers and migrate laterally along these layers, potentially impacting other improv ements located far away from the point of infiltration. Any proposed infiltration system should not be located near slopes or settlement sensitive existing/proposed improvements in order to reduce the potential for slope failures and geotechnical distress issues related to infiltration.
If water must be infiltrated due to regulato ry requirements, we recommend the absolute
Project No. 25041-01 Page 24 June 26, 2025
minimum amount of water be infiltrated and that the infiltration areas not be located near settlement-sensitive existing/proposed improvements, basement/retaining walls, or any slopes.
As with all systems that are designed to concen trate surface flow and direct the water into the subsurface soils, some minor settlement, nuisance type localized saturation and/or other water related issues should be expected. Due to variability in geologic and hydraulic conductivity characteristics, these effects ma y be experienced at the onsite location and/or potentially at other locations beyond the physical limits of the subject site. Infiltrated water may enter underground utility pipe zones or flow along heterogeneous soil layers or geologic structure and migrate laterally impacting other improvements which may be located far away or at an elevation much lower than the infiltration source. Recommendations for subsurface water infiltration are provided below.
The design infiltration rate is determined by dividing the infiltration rate by total reduction factor. The total reduction factor is calculated from a series of reduction factors, including; test procedure (RFt), site variability (RF v) and long-term siltation plugging and maintenance (RF s) as presented listed in Table 4 below (RF t + RFv + RFs). Based on the Los Angeles County testing guidelines (2021), the reduction factor for long-term siltation plugging and maintenance (RF s) is the purview of the infiltration system designer.
TABLE 4
Shallow Surface Infiltration - Reduction Factors Applied to Infiltration Rate
Consideration Reduction Factor
Test procedure, boring percolation, RFt 1.0
Site variability, number of tests, etc., RFv 1.5
Long-term siltation plugging and maintenance, RFs TBD* Total Reduction Factor, RF = RFt + RFv + RFs TBD*
*Reduction Factor for long-term siltation plugging and maintenance to be confirmed by civil engineer
Per the requirements of the Los Angeles County testing guidelines (2021), subsurface materials shall have a design infiltration rate equal to or greater than 0.3 inches per hour. The Total Reduction Factor for test procedure, site variability considerations, and long-term siltation plugging and maintenance (RFt, RFv, and RFs) and the design infiltration rate will be determined by the civil engineer. Results of infiltration testing are provided in Appendix D.
The following should be considered for the design of any expected infiltration system.
x We recommend a minimum setback of 15 feet fr om the limits of the proposed infiltration system to structural improvements.
x W e r e c o m m e n d t h e d e s i g n o f a n y i n f i l t r a t i o n system include at leas t one redundancy or overflow system. It may be prudent to provide an overflow system directly connected to the storm drain system in order to prevent failure of the infiltration system, either as a result of lower than anticipated infiltration and/or very high flow volumes.
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x Water discharge from any infiltration systems should not occur within the zone of influence of foundation footings (column and load bearing wall locations). x An adequate setback distance be tween any infiltration facility and adjace nt property lines should be maintained.
x The infiltration values provided are based on clean water and this requires the removal of trash, debris, soil particles, etc., and on-going maintenance. Over time, siltation and plugging may reduce the infiltration rate and subsequent effectiveness of the infiltration system. It should be noted that methods to prevent this shall be the responsibility of the infiltration designer and are not the purview of the geotechnical co nsultant. If adequate measures cannot be incorporated into the de sign and maintenance of the system, then the infiltration rates may need to be further reduced. These and other factors should be considered in selecting a design infiltration rate.
x Any designed infiltration system will require routine periodic maintenance. x Contamination and environmental suitability of the site for infiltration was not evaluated by us and should be evaluated by others (environmental consultant). We only addressed the geotechnical issues associated with stormwater infiltration.
LGC Geotechnical should be provided with details for any planned required infiltration system early in the design process for geotechnical input.
4.7 Preliminary Asphal t Pavement Sections
For the purpose of these prelim inary recommendations, we have selected a preliminary design R-value of 40 (assumed) and calculated pavement sections for assumed Traffic Indices (TI) of 5.0 (or less) and 6.0. These recommendations must be confirmed with R-Value testing of representative near-surface soils at the comple tion of grading and afte r underground utilities have been installed and backfilled. Final street sections should be confirmed by the project civil engineer based upon the final design Traffic Index. Determination of the TI is not the purview of the geotechnical consultant. If requested, LGC Geotechnical will provide sections for alternate TI values. Should the city of Arcadia have more stringent requirements, updated pavement recommendations can be provided.
TABLE 5
Preliminary Pavement Sections
Assumed Traffic Index 5.0 (or less) 6.0
R -Value Subgrade 40 40
AC Thickness 4.0 inches 4.0 inches
Base Thickness 5.0 inches 7.0 inches
Due to anticipated construction traffic prior to completion of the project, we recommend that the total thickness (base course and capping course) of AC be placed at essentially the same time. Construction traffic loading on only the base course of the AC will increase the potential for pavement distress. It should be noted that co nstruction traffic such as concrete trucks will
Project No. 25041-01 Page 26 June 26, 2025
likely exceed traffic loading after completion of construction. Additionally, earth moving equipment should not be allowed to drive on pa ved surfaces. The weights of these vehicles far exceed the limits of the pavement and will cause distress, likely requiring the pavement sections to be removed and replaced.
The pavement section thicknesses provided above are considered minimum thicknesses.
Increasing the thickness of any or all of the above layers will reduce the likelihood of the pavement experiencing distress during its serv ice life. The above recommendations are based on the assumption that proper maintenance and irrigation of the areas adjacent to the roadway will occur throughout the design life of th e pavement. Failure to maintain a proper maintenance and/or irrigation program may jeopardize the integrity of the pavement.
Earthwork recommendations regarding aggregat e base and subgrade are provided in the previous Section 4.1 (Site Earthwork) and the related sub-sections of this report.
P l e a s e n o t e t h a t a s t h e g e o t e c h n i c a l c o n s u l t a n t o f r e c o r d w e w i l l o n l y b e p e r f o r m i n g temperature checks of the asphalt and testing the wet density for calculating relative compaction. We recommend obtaining the services of others if material testing and evaluation o f t h e q u a l i t y o f w o r k m a n s h i p b y t h e c o n t r a c t o r i s d e s i r e d o r r e q u i r e d b y t h e r e g u l a t o r y agency.
4.8 Soil Corrosivity
Although not corrosion engineers (LGC Geotechnical is not a corrosion consultant), several governing agencies in Southern California require the geotechnical consultant to determine the corrosion potential of soils to buried concrete and metal facilities. We therefore present the results of our testing with regard to corrosion for the use of the client and other consultants, as they determine necessary.
Results of the corrosion testing indicated a soluble sulfate content ranging from approximately 8 to 32 parts per million (ppm), chloride conten t ranging from 28 to 29 ppm, pH value range of
7.4 to 7.6, and minimum resistivity value ra nging from 13,400 to 15,410 ohm-cm. Note that based on minimum resistivity the soils are considered moderately corrosive to metallic improvements. If improvements that may be su sceptible to corrosion are proposed, it is recommended that further evaluation by a corrosion engineer be performed.
Based on our laboratory test results of representa tive site soil samples, onsite soils should be considered as having a severity categorization of “not applicable” and are designated class “S0” per ACI 318, Table 19.3.1.1 with respect to sulfates. Concrete in direct contact with the onsite soils can be designed according to ACI 318, Table 19.3.2.1 using the “S0” sulfate classification.
L a b o r a t o r y t e s t i n g m a y n e e d t o b e p e r f o r m e d a t t h e c o m p l e t i o n o f g r a d i n g b y t h e p r o j e c t corrosion engineer to further evaluate the as-graded soil corrosivity characteristics, including sulfate, chloride, pH, minimum resistivity, et c. and provide design level recommendations.
Accordingly, revision of the corrosion potential may be needed, should future test results differ substantially from the conditions reported herein. The client and/or other members of the development team should consider this during the design and planning phase of the project and formulate an appropriate course of action.
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4.9 Nonstructural Concrete Flatwork
Nonstructural concrete flatwork (such as walkwa ys, bicycle trails, patio slabs, etc.) has a potential for cracking due to changes in soil vo lume related to soil-moisture fluctuations. To reduce the potential for excessive cracking and li fting, concrete may be designed in accordance with the minimum guidelines outlined in Tabl e 6 below. These guidelines will reduce the potential for irregular cracking and promote cracking along construction joints but will not eliminate all cracking or lifting. Thickening the concrete and/or adding additional reinforcement will further reduce cosmetic distress.
TABLE 6
Nonstructural Concrete Flatwork Guidelines for Very Low Expansion Potential
Community
Sidewalks
ȋζ4 feet wide)
Patios/ Walkways
(adjacent to homes
ε4 feet
wide)
Private
Vehicular
Driveways
City Sidewalk
Curb and
Gutters
Minimum
Thickness (in.) 4 (full) 4 (full) 4 (full) City/Agency
Standard
Presoaking Wet down prior
to placing
Wet down prior
to placing
Wet down prior
to placing
City/Agency
Standard
Reinforcement
No. 3 at 24
inches on
centers
No. 3 at 24
inches on
centers
City/Agency
Standard
Thickened
Edge (in.) 8 x 8 City/Agency
Standard
Crack Control
Joints
Saw cut or deep
open tool joint to
a minimum of 1/3
the concrete
thickness
Saw cut or deep
open tool joint
to a minimum
of 1/3 the
concrete
thickness
Saw cut or deep
open tool joint
to a minimum
of 1/3 the
concrete
thickness
City/Agency
Standard
Maximum
Joint Spacing 5 feet 6 feet
10 feet or
quarter cut
whichever is
closer
City/Agency
Standard
To reduce the potential for driveways to separate from the garage slab, the builder may elect to install dowels to tie these two elements together. Similarly, future homeowners should consider the use of dowels to connect flatwork to the foundation.
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4.10 Geotechnical Plan Review
When available, project plans (g rading, foundation, retaining wall, etc.) should be reviewed by LGC Geotechnical in order to verify our ge otechnical recommendations are implemented.
Updated recommendations and/or additional fieldwork may be necessary.
4.11 Geotechnical Observation and Testing During Construction
The recommendations provided in this report are based on limited subsurface observations and geotechnical analysis. Th e interpolated subsurface conditions should be checked in the field during construction by a representative of LGC Geotechnical. Geotechnical observation and testing is required per Section 1705 of the 2022 CBC.
Geotechnical observation and/or testing should be performed by LGC Geotechnical at the following stages:
x During grading (removal bottoms, fill placement, etc.); x During retaining wall backfill and compaction;
x During utility trench backfill and compaction;
x After presoaking building pads and other concrete-flatwork subgrades, and prior to placement of aggregate base or concrete;
x Preparation of pavement subgrade and placement of aggregate base; x After building and wall footing excavation and prior to placing reinforcement and/or concrete; and
x When any unusual soil conditions are enco untered during any construction operation subsequent to issuance of this report.
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5.0 LIMITATIONS
Our services were performed using the degree of care and skill ordinarily exercised, under similar circumstances, by reputable soils engineers and geologists practicing in this or similar localities. No other warranty, expressed or implied, is made as to the conclusions and professional advice included in this report.
T h i s r e p o r t i s b a s e d o n d a t a o b t a i n e d f r o m l i m i t e d o b s e r v a t i o n s o f t h e s i t e , w h i c h h a v e b e e n extrapolated to characterize the site. While the scop e of services performed is considered suitable to adequately characterize the site geotechnical conditions relative to the proposed development, no practical evaluation can completely eliminate un certainty regarding the an ticipated geotechnical conditions in connection with a subject site. Variations may exist and conditions not observed or described in this report may be encountered during grading and construction.
T h i s r e p o r t i s i s s u e d w i t h t h e u n d e r s t a n d i n g t h a t i t i s t h e r e s p o n s i b i l i t y o f t h e o w n e r , o r o f h i s / h e r representative, to ensure that the information and recommendations contained herein are brought to the attention of the other consultants (at a minimum the civil engineer, structural engineer, landscape architect) and incorporated into their plans. The contractor should properly implement the recommendations during construction and notify the owner if they consider any of the recommendations presented herein to be unsafe, or unsuitable.
The findings of this report are valid as of the presen t date. However, changes in the conditions of a site can and do occur with the passage of time, whether they be due to natural processes or the works of man on this or adjacent properties. The findings, conclusions, and recommendations presented in this report can be relied upon only if LGC Geotechnical has the opportunity to observe the subsurface c o n d i t i o n s d u r i n g g r a d i n g a n d c o n s t r u c t i o n o f t h e p r o j e c t , i n o r d e r t o c o n f i r m t h a t o u r p r e l i m i n a r y findings are representative for the site. This report is intended exclusively for use by the client, any use of or reliance on this report by a third party shall be at such party’s sole risk.
In addition, changes in applicable or appropriat e standards may occur, whether they result from legislation or the broadening of knowledge. Accordingly, the findings of this report may be invalidated wholly or partially by changes outside our control. Therefore, this report is subject to review and modification.
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Appendix A
References
Project No. 25041-01 A-1 June 26, 2025
APPENDIX A
References
A m e r i c a n C o n c r e t e I n s t i t u t e , 2 0 1 9 , B u i l d i n g C o d e R e q u i r e m e n t s f o r S t r u c t u r a l C o n c r e t e ( A C I 3 1 8 - 1 9 ) and Commentary (ACI 318R-19).
American Society of Civil Engineers (ASCE), 2017, Minimum Design Loads for Buildings and Other Structures, ASCE/SEI 7-16, 2017.
________, 2018, Standard 7-16, Minimum Design Loads for Buildings and Associated Criteria for Buildings and Other Structures, Supplement 1, effective: December 12, 2018.
American Society for Testing and Materials (ASTM), Volume 04.08 Soil and Rock (I): D420 – D5876.
Bray, J.D., and Sancio, R. B., 2006, Assessment of Liquefaction Susceptibility of Fine-Grained Soils, Journal of Geotechnical and Geoenvironmental Engineering , ASCE, pp. 1165-1177, dated September 2006.
California Building Standards Commission, 2022, Ca lifornia Building Code, California Code of Regulations Title 24, Volumes 1 and 2, dated July 2022.
California Department of Transportation (Caltrans), 2020, Highway Design Manual, Updated March 20, 2020.
California Department of Conservation, Division of Mines and Geology (CDMG), 1998, Seismic Hazard Zone Report for the Mt. Wilson 7.5-Minute Quadrangle, Los Angeles County, California, Seismic Hazard Zone Report 030, revised January 13, 2006.
________, 1999, State of California Seismic Hazard Zones, Mt. Wilson Quadrangle, Official Map, scale:
1:24,000, dated March 25, 1999.
California Geological Survey (CGS), 2008, Califo rnia Geological Survey Special Publication 117A:
Guidelines for Evaluating and Mitigating Seismic Hazards in California.
_______, 2017, Earthquake Zones of Required Investig ation, Mount Wilson Quadrangle, dated June 15, 2017.
________, 2018, Special Publication 42: Earthquake Fault Zones, A Guide for Government Agencies, Property Owners/Developers, and Geoscience Practitioners for Assessing Fault Rupture Hazards in California, Revised 2018.
________, 2025, Earthquake Zones of Required Investigation website: CGS Earthquake Zones (ca.gov) ; retrieved June 24, 2025.
County of Los Angeles, 2021, Guidelines for Geot echnical Investigation an d Reporting Low Impact Development Stormwater Infiltration, GS200.1, dated June 30, 2021.
Project No. 25041-01 A-2 June 26, 2025
Diblee, et al, 1998, Geologic Map of the Mount Wilson & Azusa Quadrangles, Los Angeles County, California, Dibblee Geology Center Map #DF-67, Last edited 2010.
Historic Aerials, 2025, vi ewed June 24, 2025, Aerial Maps from 1952 to 2022 https://www.historicaerials.com/.
KTGY, 2025, Conceptual Site Plan, Option 5c, Colorado Place, Arcadia, California, dated May 14, 2025.
Lew, et al, 2010, Seismic Earth Pr essures on Deep Basements, Stru ctural Engineers Association of California (SEAOC) Convention Proceedings.
Pradel, Daniel, 1998, Procedure to evaluate earthquake-induced settlement in dry sandy soils, Journal of Geotechnical and Geoenvironmental Engineering, Volume 124(4), pp. 364-368, dated April and October 1998.
Structural Engineers Association of California (SEAOC), 2025, Seismic Design Maps, Retrieved June 24, 2025, from https://seismicmaps.org/
United States Geological Survey (USGS), 2014, Unif ied Hazard Tool, Dynamic: Conterminous U.S. 2014 (update)(v4.2.0), Retrieved June 24, 2025, from:
https://earthquake.usgs.gov/hazards/interactive/
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Appendix C
Laboratory Test Results
Project No. 25041-01 C-1 June 2025
APPENDIX C
Laboratory Testing Procedures and Test Results
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Sample
Location
Expansion
Index
Expansion
Potential*
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Sample
Location
Description % Passing # 200
Sieve
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Ǧʹ̷͵ͷ ʹͻ
Ǧ͵̷ʹͷ ͵
ǦͶ̷ͳǦͷ ʹͷ
APPENDIX C (Cont’d)
Laboratory Testing Procedures and Test Results
Project No. 25041-01 C-2 June 2025
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ȋDzdzȌ
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ǣ
Sample
Location
Liquid Limit
(%)
Plastic Limit
(%)
Plasticity Index
(%)
USCS Soil
Classification
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Sample
Location Sample Description
Maximum
Dry Density
(pcf)
Optimum
Moisture
Content (%)
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APPENDIX C (Cont’d)
Laboratory Testing Procedures and Test Results
Project No. 25041-01 C-3 June 2025
ǣ
ȋͶͳȌǤ
Ǧ
ǤǤ
Sample
Location
Sulfate Content
(ppm)
Sulfate Exposure
Class *
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Sample Location Chloride Content, ppm
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Sample
Location pH Minimum Resistivity
(ohms-cm)
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ǦͶ̷ͳǦͷ ǤͶ ͳ͵ǡͶͲͲ
Project Name: Tested By: GB/JD Date: 04/17/25
Project No.: Checked By: J. Ward Date: 04/30/25
Boring No.: Depth (ft.):
Sample No.: Sample Type:
Soil Identification:
Sample Diameter (in.): 2.415
Sample Thickness (in.): 1.000
Weight of Sample + ring (g): 191.83
Weight of Ring (g): 44.27
Height after consol. (in.): 0.9688
Before Test
Wt. of Wet Sample+Cont. (g): 177.47
Wt. of Dry Sample+Cont. (g): 169.32
Weight of Container (g): 39.71
Initial Moisture Content (%) 6.3
Initial Dry Density (pcf) 115.5
Initial Saturation (%): 37
Initial Vertical Reading (in.) 0.1162
After Test
Wt. of Wet Sample+Cont. (g): 256.34
Wt. of Dry Sample+Cont. (g): 237.37
Weight of Container (g): 57.28
Final Moisture Content (%) 13.97
Final Dry Density (pcf): 116.6
Final Saturation (%): 85
Final Vertical Reading (in.) 0.1507
Specific Gravity (assumed): 2.70
Water Density (pcf): 62.43
0.10 0.1165 0.9997 0.00 0.03 0.459 0.03
0.25 0.1190 0.9972 0.05 0.28 0.457 0.23
0.50 0.1209 0.9953 0.12 0.47 0.455 0.35
1.00 0.1247 0.9916 0.21 0.84 0.451 0.63
1.00 0.1250 0.9912 0.21 0.88 0.450 0.67
2.00 0.1286 0.9877 0.31 1.24 0.446 0.92
4.00 0.1346 0.9816 0.41 1.84 0.439 1.43
8.00 0.1437 0.9726 0.52 2.75 0.427 2.23
16.00 0.1603 0.9560 0.64 4.41 0.405 3.77
8.00 0.1589 0.9573 0.59 4.27 0.406 3.68
4.00 0.1573 0.9590 0.53 4.11 0.408 3.58
1.00 0.1531 0.9631 0.39 3.69 0.412 3.30
0.50 0.1507 0.9655 0.33 3.45 0.41 3.120
ONE-DIMENSIONAL CONSOLIDATION
ASTM D 2435
25041-01
Arcadia
Deformation
% of Sample
Thickness
Final
Reading
(in.)
PROPERTIES of SOILS
Ring
Void
Ratio
Pressure
(p)
(ksf) Time Dial Rdgs.
(in.)Date
Apparent
Thickness
(in.)
Load
Compliance
(%)
HS-2
R-2
Square
Root of
Time
Corrected
Deforma-
tion (%)
Olive brown silty sand (SM)
Time Readings
Elapsed
Time (min)
7.5 0.400
0.410
0.420
0.430
0.440
0.450
0.460
0.470
0.10 1.00 10.00
100.
Void Ratio
Pressure, p (ksf)
Inundate with
Tap water
Consol HS-2, R-2 @ 7.5
Initial Final Initial Final Initial Final Initial Final Soil Identification:
Boring
No.
Sample
No.
Depth
(ft.)
Moisture
Content (%)
ONE-DIMENSIONAL CONSOLIDATION
PROPERTIES of SOILS
ASTM D 2435
14.0 116.6HS-2 R-2 6.3
Olive brown silty sand (SM)
Project No.:
Arcadia
04-25
25041-01
Time Readings
0.414 37 85115.5
Degree of
Saturation (%)Dry Density (pcf)
0.460
Void Ratio
7.5 0.0000
0.2000
0.4000
0.6000
0.8000
1.0000
1.2000
0.1 1.0
Deformation Dial Reading (in.)
Log of Time (min.)
0.00 0.50
1.00 1.50
2.00 2.50
3.00 3.50
4.00 0.10 1.00 10.00 100.00
Deformation (%)
Pressure, p (ksf)
0.0000
0.2000
0.4000
0.6000
0.8000
1.0000
1.2000
0.0 10.0
Square Root of Time (min.1/2)
Inundate with
Tap water
Project Name: Arcadia Tested By: G. Bathala Date: 04/23/25 Project No.: 25041-01 Checked By: J. Ward Date: 04/30/25 Boring No.: Sample Type: 90% Remold
Sample No.: Depth (ft.): 1-5
Soil Identification:
2.415 2.415 2.415
1.000 1.000 1.000
199.35 196.45 199.23
45.39 42.26 44.97
Before Shearing
218.81 218.81 218.81
207.98 207.98 207.98
77.77 77.77 77.77
0.2626 0.2739 0.0000
0.2713 0.2884 -0.0245
After Shearing
225.12 217.32 209.92
207.21 199.34 192.80
67.40 59.14 52.64
2.70 2.70 2.70
62.43 62.43 62.43
HS-2
Dark brown silty sand (SM)
Sample Diameter(in):
Weight of Wet Sample+Cont.(gm):
Vertical Rdg.(in): Final
Vertical Rdg.(in): Initial
Sample Thickness(in.):
Weight of Sample + ring(gm):
B-1
',5(&76+($57(67
&RQVROLGDWHG'UDLQHG$670'
Water Density(pcf):
Specific Gravity (Assumed):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Ring(gm):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Wet Sample+Cont.(gm):
DS HS-2, B-1 @ 1-5
Normal Stress (kip/ft²)
Peak Shear Stress (kip/ft²)
Shear Stress @ End of Test (ksf)
Deformation Rate (in./min.)
Initial Sample Height (in.)
Diameter (in.)
Initial Moisture Content (%)
Dry Density (pcf)
Saturation (%)
Soil Height Before Shearing (in.)
Final Moisture Content (%)
04-25
Project No.: 25041-01
Sample Type:
90% Remold
Dark brown silty sand (SM)
52.7 0.9913
12.8 Arcadia',5(&76+($57(675(68/76
&RQVROLGDWHG'UDLQHG$670'
53.1 0.9755
12.2 1.000
0.912
0.777
0.0033
1.000
2.415
1.000
2.415
2.000
1.625
1.449
0.0033
4.000
3.122
2.804
0.0033
53.0 0.9855
12.8 Soil Identification:
8.32 118.4
8.32 118.2 118.4
1.000
2.415
8.32 Boring No.
Sample No.
Depth (ft)
HS-2
B-1
1-5
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DS HS-2, B-1 @ 1-5
Project Name: MWIG - Arcadia Tested By: J. Domingo Date: 06/04/25 Project No.: 25041-01 Checked By: J. Ward Date: 06/12/25 Boring No.: Sample Type: Ring
Sample No.: Depth (ft.): 7.5
Soil Identification:
2.415 2.415 2.415
1.000 1.000 1.000
175.86 176.56 178.72
45.03 45.39 42.81
Before Shearing
172.82 172.82 172.82
165.19 165.19 165.19
67.11 67.11 67.11
0.2737 0.2863 0.0000
0.2903 0.3168 -0.0573
After Shearing
193.66 199.08 201.22
166.85 174.96 180.45
49.74 56.35 57.05
2.70 2.70 2.70
62.43 62.43 62.43
',5(&76+($57(67
&RQVROLGDWHG'UDLQHG$670'
Water Density(pcf):
Specific Gravity (Assumed):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Ring(gm):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Wet Sample+Cont.(gm):
HS-4
Brown silty sand with gravel (SM)g
Sample Diameter(in):
Weight of Wet Sample+Cont.(gm):
Vertical Rdg.(in): Final
Vertical Rdg.(in): Initial
Sample Thickness(in.):
Weight of Sample + ring(gm):
R-2
DS HS-4, R-2 @ 7.5
Normal Stress (kip/ft²)
Peak Shear Stress (kip/ft²)
Shear Stress @ End of Test (ksf)
Deformation Rate (in./min.)
Initial Sample Height (in.)
Diameter (in.)
Initial Moisture Content (%)
Dry Density (pcf)
Saturation (%)
Soil Height Before Shearing (in.)
Final Moisture Content (%)
104.9
1.000
2.415
7.78 Boring No.
Sample No.
Depth (ft)
HS-4
R-2
7.5 31.6
0.9695
20.3 Soil Identification:
7.78 101.2
7.78 101.0
1.185
0.0033
4.000
2.842
2.836
0.0033
1.000
0.742
0.732
0.0033
1.000
2.415
1.000
2.415
2.000
1.191
31.4 0.9834
22.9 MWIG - Arcadia
',5(&76+($57(675(68/76
&RQVROLGDWHG'UDLQHG$670'
34.6 0.9427
16.8 06-25
Project No.: 25041-01
Sample Type:
Ring
Brown silty sand with gravel
(SM)g
6KHDU6WUHVV
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DS HS-4, R-2 @ 7.5
Appendix D
Infiltration Test Results
ǣ
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ͳ ͻǣͳͲ ͻǣͶͲ ͵ͲǤͲ ǤͲͲ Ǥͷͺ ͲǤͷͺ Ǥ͵ ͲǤ
ʹ ͻǣͶͳ ͳͲǣͳͳ ͵ͲǤͲ ǤͲͲ Ǥͷͺ ͲǤͷͺ Ǥ͵ ͲǤ
͵ ͳͲǣͳͺ ͳͲǣͶͺ ͵ͲǤͲ ǤͲʹ Ǥͳ ͲǤͷͻ Ǥͷͻ ͲǤ
Ͷ ͳͲǣͷͲ ͳͳǣʹͲ ͵ͲǤͲ Ǥͻͺ Ǥͷ͵ ͲǤͷͷ Ǥ ͲǤ
ͷ ͳͳǣʹʹ ͳͳǣͷʹ ͵ͲǤͲ ǤͲʹ Ǥͳ ͲǤͷͻ Ǥͷͻ ͲǤͺ
ͳͳǣͷͶ ͳʹǣʹͶ ͵ͲǤͲ Ǥͻͺ Ǥͷʹ ͲǤͷͶ Ǥ ͲǤ
ͲǤ
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ǡǡͻʹʹǤȋͻͶͻȌ͵ͻǦͳͶͳ
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ḭ̑ʹȌ
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ǦȀǦ
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Ǧ ͺǣͶͶ ͻǣͲ ʹʹǤͲ ͳʹǤͲͷ ͳͷ ʹǤͻͷ
ͳ ͻǣͲ ͻǣͳ ͳͲǤͲ ͳͳǤͲ ͳ͵Ǥͺ͵ ʹǤͳ͵ Ǥʹ ǤͶ
ʹ ͻǣʹͲ ͻǣ͵͵ ͳ͵ǤͲ ͳͳǤͻͷ ͳͶǤ͵ͷ ʹǤͶͲ ǤͶ Ǥͻ
͵ ͻǣ͵ͺ ͻǣͶͺ ͳͲǤͲ ͳͳǤͻ͵ ͳ͵ǤͺͶ ͳǤͻͳ Ǥͺ Ǥͳ
Ͷ ͻǣͷͲ ͳͲǣͲͲ ͳͲǤͲ ͳͳǤͻʹ ͳ͵Ǥͺͺ ͳǤͻ ǤͺͲ Ǥʹ
ͷ ͳͲǣͲ͵ ͳͲǣͳ͵ ͳͲǤͲ ͳͳǤͻͶ ͳ͵ǤͺͲ ͳǤͺ Ǥ Ǥͻ
ͳͲǣͳͷ ͳͲǣʹͷ ͳͲǤͲ ͳͳǤͻͲ ͳ͵ǤͶ ͳǤͺͶ ǤͺͶ Ǥͺ
ͳͲǣʹͺ ͳͲǣ͵ͺ ͳͲǤͲ ͳͳǤͻͶ ͳ͵Ǥ ͳǤͺ͵ Ǥ Ǥͺ
ͺ ͳͲǣͶͳ ͳͲǣͷͳ ͳͲǤͲ ͳͳǤͻ͵ ͳ͵Ǥͺ ͳǤͺͷ Ǥͺ Ǥͻ
ͻ ͳͲǣͷͶ ͳͳǣͲͶ ͳͲǤͲ ͳͳǤͻʹ ͳ͵Ǥͺʹ ͳǤͻͲ ǤͺͲ ǤͲ
ͳͲ ͳͳǣͲ ͳͳǣͳ ͳͲǤͲ ͳͳǤͻͺ ͳ͵Ǥͺͳ ͳǤͺ͵ Ǥ Ǥͻ
ͳͳ ͳͳǣʹͲ ͳͳǣ͵Ͳ ͳͲǤͲ ͳͳǤͻʹ ͳ͵Ǥͺ ͳǤͺͺ ǤͺͲ Ǥͻ
ͳʹ ͳͳǣ͵͵ ͳͳǣͶ͵ ͳͲǤͲ ͳͳǤͻʹ ͳ͵Ǥͺ ͳǤͺͺ ǤͺͲ Ǥͻ
Ǥͻ
ǣ ǣ
ȋ
Ȍ
ǡ
ͳ͵ͳ
ǡǡͻʹʹǤȋͻͶͻȌ͵ͻǦͳͶͳ
ǣ
Ǧ
ǣ ʹͷͲͶͳǦͲͳ
ǣ ͶȀͳͷȀʹͲʹͷ
Ǧʹ
ȋȌȗǣ ȋȌǣ
ȋ
Ȍǣ ȋȌǣ
ȋ
Ȍǣ ȋȌǣ
ȗ
ǣȀʹʹȀʹͲʹ͵
͵Ͳ
Ǥ
ȋʹͶǣ
Ȍ
ȋʹͶǣ
Ȍ
ǡ
ȋȌ
ǡ
ȋȌ
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ȋȌ
ǡ
ȋȌ
ḭ̑ʹȌ
ȋȀȌ
ǣͲȀʹͲʹͳ
>ŽĐĂƚŝŽŶ͗
dĞƐƚŚŽůĞĚŝŵĞŶƐŝŽŶƐ;ŝĨĐŝƌĐƵůĂƌͿ
ϭϱ
ϴ
ϯ
WƌĞͲ^ŽĂŬͬWƌĞͲdĞƐƚ
EŽ͘ ^ƚĂƌƚdŝŵĞ
;Ϯϰ͗,ZͿ
^ƚŽƉdŝŵĞ
;Ϯϰ͗,ZͿ
dŝŵĞ/ŶƚĞƌǀĂů
;ŵŝŶͿ
/ŶŝƚŝĂůĞƉƚŚƚŽ
tĂƚĞƌ;ĨĞĞƚͿ
&ŝŶĂůĞƉƚŚ
ƚŽtĂƚĞƌ;ĨĞĞƚͿ
dŽƚĂůŚĂŶŐĞ
ŝŶtĂƚĞƌ>ĞǀĞů
;ĨĞĞƚͿ
WƌĞͲdĞƐƚ ϳ͗Ϯϯ ϳ͗ϱϯ ϯϬ͘Ϭ ϭϯ͘ϵϵ ϭϰ͘ϳϵ Ϭ͘ϴ
DĂŝŶdĞƐƚĂƚĂ
ϭ ϳ͗ϱϴ ϴ͗Ϯϴ ϯϬ͘Ϭ ϭϭ͘ϵϭ ϭϰ͘ϯϴ Ϯ͘ϰϳ ϲ͘ϴϮ ϯ͘Ϭ
Ϯ ϴ͗ϯϮ ϴ͗ϰϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϱϵ ϭ͘ϲϯ ϲ͘ϳϮ ϲ͘ϭ
ϯ ϴ͗ϰϱ ϴ͗ϱϱ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϳ ϭ͘ϱϮ ϲ͘ϳϰ ϱ͘ϳ
ϰ ϴ͗ϱϳ ϵ͗Ϭϳ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϰϰ ϭ͘ϰϴ ϲ͘ϳϮ ϱ͘ϱ
ϱ ϵ͗Ϭϵ ϵ͗ϭϵ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϵ ϭ͘ϱϰ ϲ͘ϳϰ ϱ͘ϳ
ϲ ϵ͗ϮϮ ϵ͗ϯϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϰϭ ϭ͘ϰϱ ϲ͘ϳϮ ϱ͘ϰ
ϳ ϵ͗ϯϰ ϵ͗ϰϰ ϭϬ͘Ϭ ϭϭ͘ϵϵ ϭϯ͘ϯϴ ϭ͘ϯϵ ϲ͘ϲϱ ϱ͘ϯ
ϴ ϵ͗ϰϱ ϵ͗ϱϱ ϭϬ͘Ϭ ϭϭ͘ϵϴ ϭϯ͘ϰϰ ϭ͘ϰϲ ϲ͘ϲϳ ϱ͘ϱ
ϵ ϵ͗ϱϴ ϭϬ͗Ϭϴ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϳ ϭ͘ϱϮ ϲ͘ϳϰ ϱ͘ϳ
ϭϬ ϭϬ͗ϭϮ ϭϬ͗ϮϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϰϮ ϭ͘ϰϲ ϲ͘ϳϮ ϱ͘ϱ
ϭϭ ϭϬ͗Ϯϰ ϭϬ͗ϯϰ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϬ ϭ͘ϰϱ ϲ͘ϳϰ ϱ͘ϰ
ϭϮ ϭϬ͗ϯϲ ϭϬ͗ϰϲ ϭϬ͘Ϭ ϭϭ͘ϵϭ ϭϯ͘ϯϮ ϭ͘ϰϭ ϲ͘ϴϮ ϱ͘Ϯ
ϭϯ ϭϬ͗ϱϵ ϭϭ͗Ϭϵ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϯ͘ϯϵ ϭ͘ϰϮ ϲ͘ϳϬ ϱ͘ϯ
ϭϰ ϭϭ͗ϭϮ ϭϭ͗ϮϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϯϳ ϭ͘ϰϭ ϲ͘ϳϮ ϱ͘ϯ
ϭϱ ϭϭ͗Ϯϰ ϭϭ͗ϯϰ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϯ͘ϯϱ ϭ͘ϯϴ ϲ͘ϳϬ ϱ͘Ϯ
ϭϲ ϭϭ͗ϯϲ ϭϭ͗ϰϲ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰ ϭ͘ϰϱ ϲ͘ϳϰ ϱ͘ϰ
ϱ͘ϯ
d
d
^ŬĞƚĐŚ͗ EŽƚĞƐ͗
ZĂǁ
WĞƌĐŽůĂƚŝŽŶ
ZĂƚĞ;ŝŶͬŚƌͿ
/ŶĨŝůƚƌĂƚŝŽŶZĂƚĞ
&ĂĐƚŽƌŽĨ^ĂĨĞƚLJ
ĞƐŝŐŶ/ŶĨŝůƚƌĂƚŝŽŶZĂƚĞ
ĂƐĞĚŽŶ'ƵŝĚĞůŝŶĞƐĨƌŽŵ͗>ŽƵŶƚLJĚĂƚĞĚϬϲͬϮϬϮϭ
^ƉƌĞĂĚƐŚĞĞƚZĞǀŝƐĞĚŽŶ͗ϲͬϮϮͬϮϬϮϯ
ŽŵŵĞŶƚƐ
dƌŝĂůEŽ͘ ^ƚĂƌƚdŝŵĞ
;Ϯϰ͗,ZͿ
^ƚŽƉdŝŵĞ
;Ϯϰ͗,ZͿ
dŝŵĞ/ŶƚĞƌǀĂů͕
Δƚ;ŵŝŶͿ
/ŶŝƚŝĂůĞƉƚŚƚŽ
tĂƚĞƌ͕Ž
;ĨĞĞƚͿ
&ŝŶĂůĞƉƚŚƚŽ
tĂƚĞƌ͕Ĩ
;ĨĞĞƚͿ
ŚĂŶŐĞŝŶ
tĂƚĞƌ>ĞǀĞů͕
Δ;ĨĞĞƚͿ
^ƵƌĨĂĐĞƌĞĂŽĨ
dĞƐƚ^ĞĐƚŝŽŶ
;ĨĞĞƚΔϮͿ
ΎŵĞĂƐƵƌĞĚĂƚƚŝŵĞŽĨƚĞƐƚ
ŽƌŝŶŐĞƉƚŚ;ĨĞĞƚͿΎ͗ WŝƚĞƉƚŚ;ĨĞĞƚͿ͗
ŽƌŝŶŐŝĂŵĞƚĞƌ;ŝŶĐŚĞƐͿ͗ Wŝƚ>ĞŶŐƚŚ;ĨĞĞƚͿ͗
WŝƉĞŝĂŵĞƚĞƌ;ŝŶĐŚĞƐͿ͗ WŝƚƌĞĂĚƚŚ;ĨĞĞƚͿ͗
ĂƚĞ͗ ϱͬϮϵͬϮϬϮϱ
/Ͳϯ
dĞƐƚƉŝƚĚŝŵĞŶƐŝŽŶƐ;ŝĨƌĞĐƚĂŶŐƵůĂƌͿ
/ŶĨŝůƚƌĂƚŝŽŶdĞƐƚĂƚĂ^ŚĞĞƚ
>''ĞŽƚĞĐŚŶŝĐĂů͕/ŶĐ
ϭϯϭĂůůĞ/ŐůĞƐŝĂ^ƵŝƚĞ͕^ĂŶůĞŵĞŶƚĞ͕ϵϮϲϳϮƚĞů͘;ϵϰϵͿϯϲϵͲϲϭϰϭ WƌŽũĞĐƚEĂŵĞ͗ Dt/'ͲƌĐĂĚŝĂ
WƌŽũĞĐƚEƵŵďĞƌ͗ ϮϱϬϰϭͲϬϭ
>ŽĐĂƚŝŽŶ͗
dĞƐƚŚŽůĞĚŝŵĞŶƐŝŽŶƐ;ŝĨĐŝƌĐƵůĂƌͿ
ϭϱ
ϴ
ϯ
WƌĞͲ^ŽĂŬͬWƌĞͲdĞƐƚ
EŽ͘ ^ƚĂƌƚdŝŵĞ
;Ϯϰ͗,ZͿ
^ƚŽƉdŝŵĞ
;Ϯϰ͗,ZͿ
dŝŵĞ/ŶƚĞƌǀĂů
;ŵŝŶͿ
/ŶŝƚŝĂůĞƉƚŚƚŽ
tĂƚĞƌ;ĨĞĞƚͿ
&ŝŶĂůĞƉƚŚ
ƚŽtĂƚĞƌ;ĨĞĞƚͿ
dŽƚĂůŚĂŶŐĞ
ŝŶtĂƚĞƌ>ĞǀĞů
;ĨĞĞƚͿ
WƌĞͲdĞƐƚ ϴ͗Ϭϳ ϴ͗ϯϳ ϯϬ͘Ϭ ϭϮ͘ϭϱ ϭϰ͘Ϯ Ϯ͘Ϭϱ
DĂŝŶdĞƐƚĂƚĂ
ϭ ϴ͗ϯϵ ϴ͗ϰϵ ϭϬ͘Ϭ ϭϭ͘ϰϰ ϭϮ͘ϵϰ ϭ͘ϱϬ ϳ͘ϴϭ ϰ͘ϴ
Ϯ ϴ͗ϱϬ ϵ͗ϬϬ ϭϬ͘Ϭ ϭϭ͘ϵϯ ϭϯ͘Ϭϵ ϭ͘ϭϲ ϲ͘ϳϴ ϰ͘ϯ
ϯ ϵ͗ϬϮ ϵ͗ϭϮ ϭϬ͘Ϭ ϭϭ͘ϴϱ ϭϮ͘ϵϮ ϭ͘Ϭϳ ϲ͘ϵϱ ϯ͘ϵ
ϰ ϵ͗ϭϰ ϵ͗ϱϬ ϯϲ͘Ϭ ϭϭ͘ϵϱ ϭϰ͘Ϭϳ Ϯ͘ϭϮ ϲ͘ϳϰ Ϯ͘Ϯ
ϱ ϵ͗ϱϯ ϭϬ͗Ϭϯ ϭϬ͘Ϭ ϭϭ͘ϴϬ ϭϮ͘ϵϴ ϭ͘ϭϴ ϳ͘Ϭϱ ϰ͘Ϯ
ϲ ϭϬ͗Ϭϱ ϭϬ͗ϭϱ ϭϬ͘Ϭ ϭϭ͘ϵϯ ϭϯ͘ϬϬ ϭ͘Ϭϳ ϲ͘ϳϴ ϰ͘Ϭ
ϳ ϭϬ͗ϭϴ ϭϬ͗Ϯϴ ϭϬ͘Ϭ ϭϭ͘ϵϴ ϭϯ͘ϭϬ ϭ͘ϭϮ ϲ͘ϲϳ ϰ͘Ϯ
ϴ ϭϬ͗ϯϮ ϭϬ͗ϰϮ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϯ͘ϭϮ ϭ͘ϭϱ ϲ͘ϳϬ ϰ͘ϯ
ϵ ϭϭ͗Ϭϲ ϭϭ͗ϭϲ ϭϬ͘Ϭ ϭϭ͘ϴϮ ϭϮ͘ϴϮ ϭ͘ϬϬ ϳ͘Ϭϭ ϯ͘ϲ
ϭϬ ϭϭ͗ϭϴ ϭϭ͗Ϯϴ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϮ͘ϴϲ Ϭ͘ϵϭ ϲ͘ϳϰ ϯ͘ϰ
ϭϭ ϭϭ͗ϯϬ ϭϭ͗ϰϬ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϮ͘ϵϵ ϭ͘ϬϮ ϲ͘ϳϬ ϯ͘ϴ
ϭϮ ϭϭ͗ϰϯ ϭϭ͗ϱϯ ϭϬ͘Ϭ ϭϭ͘ϵϴ ϭϯ͘Ϭϰ ϭ͘Ϭϲ ϲ͘ϲϳ ϰ͘Ϭ
ϭϯ ϭϭ͗ϱϳ ϭϮ͗Ϭϳ ϭϬ͘Ϭ ϭϭ͘ϵϯ ϭϯ͘Ϭϱ ϭ͘ϭϮ ϲ͘ϳϴ ϰ͘Ϯ
ϭϰ ϭϮ͗Ϭϵ ϭϮ͗ϭϵ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϭϬ ϭ͘ϭϱ ϲ͘ϳϰ ϰ͘ϯ
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Appendix E
General Earthwork & Grading Specifications
for Rough Grading
General Earthwork and Grading Specifications for Rough Grading
1.0 General
1.1 Intent
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1.2 The Geotechnical Consultant of Record
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1.3 The Earthwork Contractor
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2.0 Preparation of Areas to be Filled
2.1 Clearing and Grubbing
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2.2 Processing
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2.3 Ove r-excavation
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2.4 Benching
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2.5 Evaluation/Acceptance of Fill Areas
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3.0 Fill Material
3.1 General
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3.2 Oversize
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3.3 Import
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4.0 Fill Placement and Compaction
4.1 Fill Layers
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General Earthwork and Grading Specifications for Rough Grading Page 4
4.6 Frequency of Compaction Testing
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4.7 Compaction Test Locations
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5.0 Subdrain Installation
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Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/LID/Preliminary/MWIG-010 - DMA P1.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID DMA P1
Area (ac) 2.62
Flow Path Length (ft) 680.25
Flow Path Slope (vft/hft) 0.0105
85th Percentile Rainfall Depth (in) 1.0
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 85th percentile storm
Fire Factor 0
LID True
Output Results
Modeled (85th percentile storm) Rainfall Depth (in) 1.0 Peak Intensity (in/hr) 0.2531
Undeveloped Runoff Coefficient (Cu) 0.1
Developed Runoff Coefficient (Cd) 0.788
Time of Concentration (min) 31.0
Clear Peak Flow Rate (cfs) 0.5225
Burned Peak Flow Rate (cfs) 0.5225
24-Hr Clear Runoff Volume (ac-ft) 0.1706
24-Hr Clear Runoff Volume (cu-ft) 7432.5072
Peak Flow Hydrologic Analysis
File location: P:/M/MWIG-010/Admin/Reports/LID/Preliminary/MWIG-010 - DMA P2.pdf Version: HydroCalc 1.0.3
Input Parameters
Project Name MWIG-010
Subarea ID DMA P2
Area (ac) 1.08
Flow Path Length (ft) 257.17
Flow Path Slope (vft/hft) 0.005
85th Percentile Rainfall Depth (in) 1.0
Percent Impervious 0.86
Soil Type 7
Design Storm Frequency 85th percentile storm
Fire Factor 0
LID True
Output Results
Modeled (85th percentile storm) Rainfall Depth (in) 1.0 Peak Intensity (in/hr) 0.3186
Undeveloped Runoff Coefficient (Cu) 0.1
Developed Runoff Coefficient (Cd) 0.788
Time of Concentration (min) 19.0
Clear Peak Flow Rate (cfs) 0.2711
Burned Peak Flow Rate (cfs) 0.2711
24-Hr Clear Runoff Volume (ac-ft) 0.0703
24-Hr Clear Runoff Volume (cu-ft) 3063.758
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TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-43 December 20, 2013
INF-7: Underground Infiltration
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infiltration products that allow for similar or enhanced rates of infiltration and subsurface storage while offering durable prefrabricated structures. There are many varieties of
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Source: http://www.contech-cpi.com
TECHNICAL GUIDANCE DOCUMENT APPENDICES
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County of Los Angeles D-1 February 2014
S-1: Storm Drain Message and Signage
Purpose
Waste material dumped into storm drain inlets can adversely impact surface and ground waters. In fact, any material discharged into the storm drain system has the potential to significantly impact downstream receiving waters. Storm drain messages have become a popular method of alerting and reminding the public about the effects of and the prohibitions against waste disposal into the storm drain system. The signs are typically stenciled or affixed near the storm drain inlet or catch basin. The message simply informs the public that dumping of wastes into storm drain inlets is prohibited and/or that the drain ultimately discharges into receiving waters.
General Guidance
x The signs must be placed so they are easily visible to the public. x Be aware that signs placed on sidewalk will be worn by foot traffic.
Design Specifications
x Signs with language and/or graphical icons that prohibit illegal dumping, must be posted at designated public access points along channels and streams within the project area. Consult with Los Angeles County Department of Public Works (LACDPW) staff to determine specific signage requirements for channels and streams.
x Storm drain message markers, placards, concrete stamps, or stenciled language/icons (e.g., “No Dumping – Drains to the Ocean”) are required at all storm drain inlets and catch basins within the project area to discourage illegal or inadvertent dumping. Signs should be placed in clear sight facing anyone approaching the storm drain inlet or catch basin from either side (see Figure D-1 and Figure D-2). LACDPW staff should be contacted to determine specific requirements for types of signs and methods of application. A stencil can be purchased for a nominal fee from LACDPW Building and Safety Office by calling (626) 458-3171. All storm drain inlet and catch basin locations must be identified on the project site map.
Maintenance Requirements
Legibility and visibility of markers and signs should be maintained (e.g., signs should be repainted or replaced as necessary). If required by LACDPW, the owner/operator or homeowner’s association shall enter into a maintenance agreement with the agency or record a deed restriction upon the property title to maintain the legibility of placards and signs.
S-1: Storm Drain Message and Signage
County of Los Angeles D-2 February 2014
Figure D-1. Storm Drain Message Location – Curb Type Inlet Figure D-2. Storm Drain Message Location – Catch Basin/Area Type Inlet
CONCRETE
PERIMETER
County of Los Angeles D-19 February 2014
S-8: Landscape Irrigation Practices
Purpose
Irrigation runoff provides a pathway for pollutants (i.e., nutrients, bacteria, organics, sediment) to enter the storm drain system. By effectively irrigating, less runoff is produced resulting in less potential for pollutants to enter the storm drain system.
General Guidance
x Do not allow irrigation runoff from the landscaped area to drain directly to storm drain system.
x Minimize use of fertilizer, pesticides, and herbicides on landscaped areas. x Plan sites with sufficient landscaped area and dispersal capacity (e.g., ability to receive irrigation water without generating runoff).
x Consult a landscape professional regarding appropriate plants, fertilizer, mulching applications, and irrigation requirements (if any) to ensure healthy vegetation growth.
Design Specifications
x Choose plants that minimize the need for fertilizer and pesticides. x Group plants with similar water requirements and water accordingly. x Use mulch to minimize evaporation and erosion.
x Include a vegetative boundary around project site to act as a filter. x Design the irrigation system to only water areas that need it. x Install an approved subsurface drip, pop-up, or other irrigation system.1 The irrigation system should employ effective energy dissipation and uniform flow spreading methods to prevent erosion and facilitate efficient dispersion. x Install rain sensors to shut off the irrigation system during and after storm events. x Include pressure sensors to shut off flow-through system in case of sudden pressure drop. A sudden pressure drop may indicate a broken irrigation head or water line.
x If the hydraulic conductivity in the soil is not sufficient for the necessary water application rate, implement soil amendments to avoid potential geotechnical hazards (i.e., liquefaction, landslide, collapsible soils, and expansive soils). 1 If alternative distribution systems (e.g., spray irrigation) are approved, the County will establish guidelines to implement these new systems.
S-8: Landscape Irrigation Practices
County of Los Angeles D-20 February 2014
x For sites located on or within 50 feet of a steep slope (15% or greater), do not irrigate landscape within three days of a storm event to avoid potential geotechnical instability.
2 x Implement Integrated Pest Management practices.
For additional guidelines and requirements, refer to the Los Angeles County Department of Health Services.
Maintenance Requirements
Maintain irrigation areas to remove trash and debris and loose vegetation. Rehabilitate areas of bare soil. If a rain or pressure sensor is installed, it should be checked periodically to ensure proper function. Inspect and maintain irrigation equipment and components to ensure proper functionality. Clean equipment as necessary to prevent algae growth and vector breeding. Maintenance agreements between LACDPW and the owner/operator may be required. Failure to properly maintain building and property may subject the property owner to citation.
2 As determined by the City of Los Angeles, Building and Safety Division County of Los Angeles D-21 February 2014
S-9: Building Materials Selection
Purpose
Building materials can potentially contribute pollutants of concern to stormwater runoff through leaching. For example, metal buildings, roofing, and fencing materials may be significant sources of metals in stormwater runoff, especially due to acidic precipitation.
The use of alternative building materials can reduce pollutant sources in stormwater runoff by eliminating compounds that can leach into stormwater runoff. Alternative building materials may also reduce the need to perform maintenance activities (i.e., painting) that involve pollutants of concern, and may reduce the volume of stormwater runoff. Alternative materials are available to replace lumber and paving.
Design Specifications
Lumber
Decks and other house components constructed using pressure-treated wood that is typically treated using arsenate, copper, and chromium compounds are hazardous to the environment. Pressure-treated wood may be replaced with cement-fiber or vinyl.
Roofs, Fencing, and Metals
Minimizing the use of copper and galvanized (zinc-coated) metals on buildings and fencing can reduce leaching of these pollutants into stormwater runoff. The following building materials are conventionally made of galvanized metals:
x Metal roofs;
x Chain-link fencing and siding; and
x Metal downspouts, vents, flashing, and trim on roofs.
Architectural use of copper for roofs and gutters should be avoided. As an alternative to copper and galvanized materials, coated metal products are available for both roofing and gutter application. Vinyl-coated fencing is an alternative to traditional galvanized chain-link fences. These products eliminate contact of bare metal with precipitation or stormwater runoff, and reduce the potential for stormwater runoff contamination.
Roofing materials are also made of recycled rubber and plastic.
Green roofs may be an option. Green roofs use vegetation such as grasses and other plants as an exterior surface. The plants reduce the velocity of stormwater runoff and absorb water to reduce the volume of stormwater runoff. One potential problem with using green roofs in the Los Angeles County area is the long, hot and dry summers, which may kill the plants if they are not watered. See the Green Roof Fact Sheet (RET- 7) in Appendix E.
S-9: Building Materials Selection
County of Los Angeles D-22 February 2014
Pesticides
The use of pesticides around foundations can be reduced through the use of alternative barriers. Sand barriers can be applied around foundations to deter termites, as they cannot tunnel through sand. Metal shields also block termites from tunneling.
Additionally, diatomaceous earth can be used to repel or kill a wide variety of other pests.
Maintenance Requirements
The integrity of structural elements that are subject to damage (e.g., signs) must be maintained by the owner/operator as required by local codes and ordinances.
Maintenance agreements between LACDPW and the owner/operator may be required.
Failure to properly maintain building and property may subject the property owner to citation.
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-78 December 20, 2013
PRE-2: Catch Basin Insert Fact Sheet
Catch basin inserts are manufactured filters or fabric placed in a drop inlet to remove sediment and debris and may include sorbent media (oil absorbent pouches) to remove floating oils and grease. Catch basin inserts are selected specifically based upon the orientation of the inlet and the expected sediment and debris loading.
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Table XIV.2: Proprietary Catch Basin Insert Manufacturer Websites 'HYLFH 0DQXIDFWXUHU :HEVLWH
$E7HFK,QGXVWULHV8OWUD
Urban Filter™ $E7HFK,QGXVWULHV www.abtechindustries.com $TXDVKLHOG$TXD
Guardian™ Catch Basin
,QVHUW
Aquashield™ Inc. www.aquashieldinc.com
Bowhead StreamGuard™ %RZKHDG(QYLURQPHQWDO 6DIHW\ ,QF http://www.shopbowhead.com/
&RQWHFK7ULWRQ&DWFK
Basin Filter™
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Filter™
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Also known as:
¾ Drop Inlet Filters
¾ Catch Basin Filters
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DrainPac™
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-79 December 20, 2013
Table XIV.2: Proprietary Catch Basin Insert Manufacturer Websites 'HYLFH 0DQXIDFWXUHU :HEVLWH
&RQWHFK7ULWRQ%DVLQ
StormFilter™
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&XUE,QOHW%DVNHW 6XQ7UHH7HFKQRORJLHV,QF www.suntreetech.com &XUE,QOHW*UDWHV EcoSense International™ http://www.ecosenseint.com/ 'UDLQ3DF70 8QLWHG6WRUP:DWHU,QF http://www.unitedstormwater.com *UDWH,QOHW6NLPPHU%R[ 6XQ7UHH7HFKQRORJLHV,QF www.suntreetech.com .UL6WDU)OR*DUG3/86 .UL6WDU(QWHUSULVHV,QF www.kristar.com .UL6WDU)OR*DUG .UL6WDU(QWHUSULVHV,QF www.kristar.com .UL6WDU)OR*DUG/R3UR
0DWUL[)LOWHU .UL6WDU(QWHUSULVHV,QF www.kristar.com 1\ORSODVW6WRUP385(
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Drain Inserts MP-52
January 2003 California Stormwater BMP Handbook 1 of 3
New Development and Redevelopment
www.cabmphandbooks.com
Description
Drain inserts are manufactured filters or fabric placed in a drop inlet to remove sediment and debris. There are a multitude of inserts of various shapes and configurations, typically falling into one of three different groups: socks, boxes, and trays. The sock consists of a fabric, usually constructed of polypropylene. The fabric may be attached to a frame or the grate of the inlet holds the sock. Socks are meant for vertical (drop) inlets. Boxes are constructed of plastic or wire mesh. Typically a polypropylene “bag” is placed in the wire mesh box. The bag takes the form of the box. Most box products are one box; that is, the setting area and filtration through media occur in the same box. Some products consist of one or more trays or mesh grates. The trays may hold different types of media. Filtration media vary by manufacturer. Types include polypropylene, porous polymer, treated cellulose, and activated carbon.
California Experience
The number of installations is unknown but likely exceeds a thousand. Some users have reported that these systems require considerable maintenance to prevent plugging and bypass.
Advantages
Does not require additional space as inserts as the drain inlets are already a component of the standard drainage systems.
Easy access for inspection and maintenance.
As there is no standing water, there is little concern for mosquito breeding.
A relatively inexpensive retrofit option.
Limitations
Performance is likely significantly less than treatment systems that are located at the end of the drainage system such as ponds and vaults. Usually not suitable for large areas or areas with trash or leaves than can plug the insert.
Design and Sizing Guidelines
Refer to manufacturer’s guidelines. Drain inserts come any many configurations but can be placed into three general groups:
socks, boxes, and trays. The sock consists of a fabric, usually constructed of polypropylene. The fabric may be attached to a frame or the grate of the inlet holds the sock. Socks are meant for vertical (drop) inlets. Boxes are constructed of plastic or wire mesh. Typically a polypropylene “bag” is placed in the wire mesh box. The bag takes the form of the box. Most box products are Design Considerations
Use with other BMPs
Fit and Seal Capacity within Inlet
Targeted Constituents
Sediment
Nutrients
Trash
Metals
Bacteria
Oil and Grease
Organics
Removal Effectiveness
See New Development and
Redevelopment Handbook-Section 5.
MP-52 Drain Inserts
2 of 3 California Stormwater BMP Handbook January 2003
New Development and Redevelopment
www.cabmphandbooks.com
one box; that is, the setting area and filtration through media occurs in the same box. One manufacturer has a double-box. Stormwater enters the first box where setting occurs. The stormwater flows into the second box where the filter media is located. Some products consist of one or more trays or mesh grates. The trays can hold different types of media. Filtration media vary with the manufacturer: types include polypropylene, porous polymer, treated cellulose, and activated carbon.
Construction/Inspection Considerations
Be certain that installation is done in a manner that makes certain that the stormwater enters the unit and does not leak around the perimeter. Leakage between the frame of the insert and the frame of the drain inlet can easily occur with vertical (drop) inlets.
Performance
Few products have performance data collected under field conditions.
Siting Criteria
It is recommended that inserts be used only for retrofit situations or as pretreatment where other treatment BMPs presented in this section area used.
Additional Design Guidelines
Follow guidelines provided by individual manufacturers.
Maintenance
Likely require frequent maintenance, on the order of several times per year.
Cost
The initial cost of individual inserts ranges from less than $100 to about $2,000. The cost of using multiple units in curb inlet drains varies with the size of the inlet.
The low cost of inserts may tend to favor the use of these systems over other, more effective treatment BMPs. However, the low cost of each unit may be offset by the number of units that are required, more frequent maintenance, and the shorter structural life (and therefore replacement).
References and Sources of Additional Information
Hrachovec, R., and G. Minton, 2001, Field testing of a sock-type catch basin insert, Planet CPR, Seattle, Washington
Interagency Catch Basin Insert Committee, Evaluation of Commercially-Available Catch Basin Inserts for the Treatment of Stormwater Runoff from Developed Sites, 1995 Larry Walker Associates, June 1998, NDMP Inlet/In-Line Control Measure Study Report Manufacturers literature
Santa Monica (City), Santa Monica Bay Municipal Stormwater/Urban Runoff Project - Evaluation of Potential Catch basin Retrofits, Woodward Clyde, September 24, 1998 Drain Inserts MP-52
January 2003 California Stormwater BMP Handbook 3 of 3
New Development and Redevelopment
www.cabmphandbooks.com
Woodward Clyde, June 11, 1996, Parking Lot Monitoring Report, Santa Clara Valley Nonpoint Source Pollution Control Program.
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Wipe pots, pans,
and work areas
prior to washing.
Do not pour
cooking residue
directly into
the drain.
Do not pour waste
oil directly into the
drain, parking lot
or street.
Do not wash floor
mats outside where
water will run off
directly into the
storm drain.
Do not rinse spills
into the street.
1 2
2 3
3 4
41 Dispose of food
waste directly
into the trash.
Avoid using the
garbage disposal.
Place greasy food
in the trash.
Clean mats inside
over a utility sink.
Use dry clean up
for spills.
Collect waste
oil and store
for recycling.
THE
RIGHT WAY
THE
WRONG WAY
Good Cleaning Practices
Managing FATS, OIL and GREASE
POST IN CLEANUP/ WORK AREA
www.lacsd.org
PUBLIC WORKS
County of Los Angeles Department of Public Works
For more information call (888) CLEAN LA or visit www.888CleanLA.com Are You a Litter Bug Are You a Litter Bug
and and DoDon’t Know It?t Know It?
Take our quiz!
Have you ever...
• Dropped a cigarette butt or trash on the ground?
• Failed to pick up after your dog while out on a walk? • Overwatered your lawn after applying
fertilizers/pesticides?
• Disposed of used motor oil in the street,
gutter or garbage?
If you answered yes to any of these actions, then
YOU ARE A LITTER BUG
!
Each of these behaviors contribute to stormwater
pollution, which contaminates our ocean and
waterways, kills marine life and causes beach closures.
You can become part of the solution!
To find out how, flip this card over.
For more information, call or visit:
Follow these simple steps to
prevent stormwater pollution
• Put your garbage where it belongs — in the trash can. • Pick up after your dog when out on a walk.
• Reduce pesticide and fertilizer use; don’t overwater after application or apply if rain is forecast.
• Dispose of used motor oil at an oil recycling center or at a free Household Hazardous Waste/E-Waste
collection event.
A message from the County of Los Angeles Department of Public Works.Printed on recycled paper.
Follow these simple steps to Follow these simple steps to prevent stormwater pollution:prevent stormwater pollution:
DoDon’t Paint the’t Paint the Town Red!Town Red!
Storm drains are for rain…
they’re not for paint disposal.
More than 197,000 times each month, L.A. County residents wash their dirty paint brushes under an outdoor faucet.
This dirty rinse water flows into the street, down the
storm drain and straight to the ocean — untreated.
Remember to clean water-based paint brushes in the
sink, rinse oil-based paint brushes with paint thinner, and take old paint and paint-related products to a Household Hazardous Waste/E-Waste collection event.
Tips for Paint Clean-Up:
L.A. County residents can help solve the stormwater
pollution problem by taking these easy steps when
working with paint and paint-related products…
• Never dispose of paint or paint-related products in the gutters or storm drains. This is called illegal dumping.
Take them to a Household Hazardous Waste/E-Waste
collection event. Call 1 (888) CLEAN LA or visit
www.888CleanLA.com to locate an event near you.
• Buy only what you need. Reuse leftover paint for
touch-ups or donate it to a local graffiti abatement
program. Recycle or use excess paint.
• Clean water-based paint brushes in the sink.
• Oil-based paints should be cleaned with paint thinner.
Filter and reuse paint thinner. Set the used thinner
aside in a closed jar to settle-out paint particles.
• Store paints and paint-related products in rigid,
durable and watertight containers with
tight-fitting covers.
A message from the County of Los Angeles Department of Public Works.Printed on recycled paper.
Storm drains are for rain…
they’re not pooper scoopers.
L.A. County residents walk a dog without picking up
the droppings more than 62,000 times per month.
Disease-causing dog waste washes from the
ground and streets into storm drains and
flows straight to the ocean — untreated.
Remember to bring a bag and
clean up after your dog.
PPickick UpUp AfterAfter YourYour Pooch!Pooch!
Dog owners can help solve the stormwater pollution
problem by taking these easy steps…
• Clean up after your dog every single time.
• Take advantage of the complimentary waste bags
offered in dispensers at local parks.
• Ensure you always have extra bags in your car so
you are prepared when you travel with your dog.
• Carry extra bags when walking your dog and make
them available to other pet owners who are without.
• Teach children how to properly clean up after a pet.
Encourage them to throw the used bags in the
nearest trash receptacle if they are away from home.
• Put a friendly message on the bulletin board at
the local dog park to remind pet owners to clean
up after their dogs.
• Tell friends and neighbors about the ill effects of animal waste on the environment. Encourage
them to clean up after their pets as well.
Tips for Dog Owners:
Are You a Litter Bug Are You a Litter Bug
and and DoDon’t Know It?t Know It?
Take our quiz!
Have you ever...
• Dropped a cigarette butt or trash on the ground?
• Failed to pick up after your dog while out on a walk? • Overwatered your lawn after applying
fertilizers/pesticides?
• Disposed of used motor oil in the street,
gutter or garbage?
If you answered yes to any of these actions, then
YOU ARE A LITTER BUG
!
Each of these behaviors contribute to stormwater
pollution, which contaminates our ocean and
waterways, kills marine life and causes beach closures.
You can become part of the solution!
To find out how, flip this card over.
For more information, call or visit:
Follow these simple steps to
prevent stormwater pollution
• Put your garbage where it belongs — in the trash can. • Pick up after your dog when out on a walk.
• Reduce pesticide and fertilizer use; don’t overwater after application or apply if rain is forecast.
• Dispose of used motor oil at an oil recycling center or at a free Household Hazardous Waste/E-Waste
collection event.
A message from the County of Los Angeles Department of Public Works.Printed on recycled paper.
Follow these simple steps to Follow these simple steps to prevent stormwater pollution:prevent stormwater pollution:
Swimming
Pool Tips
Make sure all
chemicals are
dissipated before
draining a pool or
spa
Do not drain pools
within 5 days of
adding chemicals
Never backwash a
filter into the street
or stormdrain
Cleanup chemical
spills with
absorbent, don’t
wash it down the
drain
Dispose of leftover
chemicals and paints
through a licensed
hazardous waste
disposal provider
Follow these simple steps to
prevent stormwater pollution…
SStormdrains
take runoff
directly to creeks
and the ocean without treatment.
Pool chemicals can harm our
natural creeks and waterways.
Anything going into our
stormdrains that isn’t
rainwater contributes to
stormwater pollution, which
contaminates our creeks and
ocean, kills marine life and
causes beach closures.
...not pool chemicals
Storm Drains are
for Rain...
S
AA YardYard is ais a Terrible Terrible
ThingThing toto Waste!Waste!
Storm drains are for rain…not yard waste.
Residential yard waste represents about 13 percent
of the total waste generated in L.A. County.
Pesticides, fertilizer and yard waste such as leaves and mowed grass wash from the ground and streets into storm drains and flow straight to the ocean — untreated.
Remember to use pesticides and fertilizer
wisely and pick-up yard waste.
Tips For Yard Care:
L.A. County residents can help solve the stormwater
pollution problem by taking these easy steps…
• Do not over-fertilize and do not use fertilizer or pesticides near ditches, gutters or storm drains.
• Do not use fertilizer or pesticides before a rain.
• Follow the directions on the label carefully.
• Use pesticides sparingly — more is not better.
“Spot” apply, rather than “blanket” apply.
• When watering your lawn, use the least amount of
water possible so it doesn’t run into the street carrying pesticides and other chemicals with it.
• Use non-toxic products for your garden and lawn
whenever possible.
• If you must store pesticides or fertilizer, make sure they are in a sealed, water-proof container in a
covered area to prevent runoff.
• Do not blow, sweep, hose or rake leaves or other
yard trimmings into the street, gutter or storm drain.
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dŽďĞĚĞƚĞƌŵŝŶĞĚ
WĂŐĞϮŽĨϵ
KƉĞƌĂƚŝŽŶƐĂŶĚDĂŝŶƚĞŶĂŶĐĞWůĂŶ
DW
ƉƉůŝĐĂďůĞ͍
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DWEĂŵĞĂŶĚDW/ŵƉůĞŵĞŶƚĂƚŝŽŶ͕DĂŝŶƚĞŶĂŶĐĞ͕ĂŶĚ
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/ŵƉůĞŵĞŶƚĂƚŝŽŶ͕DĂŝŶƚĞŶĂŶĐĞ͕ĂŶĚ
/ŶƐƉĞĐƚŝŽŶ&ƌĞƋƵĞŶĐLJĂŶĚ^ĐŚĞĚƵůĞ
WĞƌƐŽŶŽƌ
ŶƚŝƚLJǁŝƚŚ
KƉĞƌĂƚŝŽŶĂŶĚDĂŝŶƚĞŶĂŶĐĞ
ZĞƐƉŽŶƐŝďŝůŝƚLJ
EŽŶͲ^ƚƌƵĐƚƵƌĂů^ŽƵƌĐĞŽŶƚƌŽůDWƐ
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Eϭ͘
ĚƵĐĂƚŝŽŶĨŽƌWƌŽƉĞƌƚLJKǁŶĞƌƐ͕dĞŶĂŶƚƐ͕ĂŶĚKĐĐƵƉĂŶƚƐ
dŚŝƐǁŝůůďĞĂĚĚƌĞƐƐĞĚƚŚƌŽƵŐŚĞĚƵĐĂƚŝŽŶĂůŵĂƚĞƌŝĂůƐ͘ůů ŝŶĐůƵĚĞĚŵĂƚĞƌŝĂůƐƉƌŽǀŝĚĞǁĂLJƐŽĨŵŝƚŝŐĂƚŝŶŐƐƚŽƌŵǁĂƚĞƌ ƉŽůůƵƚŝŽŶŝŶĞǀĞƌLJĚĂLJĂĐƚŝǀŝƚŝĞƐĂƐƐŽĐŝĂƚĞĚǁŝƚŚƌĞƐŝĚĞŶƚƐĂƐǁĞůů ĂƐĞŵƉůŽLJĞĞƐŽĨƚŚĞƉƌŽƉĞƌƚLJŵĂŶĂŐĞŵĞŶƚĐŽŵƉĂŶLJĂŶĚƚŚĞŝƌ ƐƵďͲĐŽŶƚƌĂĐƚŽƌƐ͘WƌĂĐƚŝĐĂůŝŶĨŽƌŵĂƚŝŽŶĂůŵĂƚĞƌŝĂůƐĂƌĞƉƌŽǀŝĚĞĚ ƚŽƌĞƐŝĚĞŶƚƐ͕ŽĐĐƵƉĂŶƚƐ͕ŽƌƚĞŶĂŶƚƐƚŽŝŶĐƌĞĂƐĞƚŚĞƉƵďůŝĐ͛Ɛ ƵŶĚĞƌƐƚĂŶĚŝŶŐŽĨƐƚŽƌŵǁĂƚĞƌƋƵĂůŝƚLJ͕ƐŽƵƌĐĞƐŽĨƉŽůůƵƚĂŶƚƐ͕ĂŶĚ ǁŚĂƚƚŚĞLJĐĂŶĚŽƚŽƌĞĚƵĐĞƉŽůůƵƚĂŶƚƐŝŶƐƚŽƌŵǁĂƚĞƌ͘
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ZƚŽƉƌŽǀŝĚĞĞĚƵĐĂƚŝŽŶĂů
ŵĂƚĞƌŝĂůƐ͕ĂĐŽƉLJŽĨƚŚĞĂƉƉƌŽǀĞĚtYDW
ĂŶĚKƉĞƌĂƚŝŽŶΘDĂŝŶƚĞŶĂŶĐĞWůĂŶ;KΘDͿ
ƚŽŶĞǁƉƌŽƉĞƌƚLJŽǁŶĞƌƐ͕ƚĞŶĂŶƚƐ͕ŽĐĐƵƉĂŶƚƐ
ΘĞŵƉůŽLJĞĞƐ͕ĂƚƚŝŵĞŽĨŚŝƌĞ͕ůĞĂƐŝŶŐĂŶĚͬŽƌ
ŚŽŵĞƉƵƌĐŚĂƐĞ͘
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ZzĞƐ
EϮ͘ĐƚŝǀŝƚLJZĞƐƚƌŝĐƚŝŽŶ
ZƵůĞƐŽƌŐƵŝĚĞůŝŶĞƐĨŽƌĚĞǀĞůŽƉŵĞŶƚƐĂƌĞĞƐƚĂďůŝƐŚĞĚǁŝƚŚŝŶƚŚĞ ĂƉƉƌŽƉƌŝĂƚĞĚŽĐƵŵĞŶƚƐǁŚŝĐŚƉƌŽŚŝďŝƚĂĐƚŝǀŝƚŝĞƐƚŚĂƚĐĂŶƌĞƐƵůƚ ŝŶĚŝƐĐŚĂƌŐĞƐŽĨƉŽůůƵƚĂŶƚƐ͘
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ZĞŵƉůŽLJĞĞƐŶŽƚŝĨŝĞĚŽĨ
ĂĐƚŝǀŝƚŝĞƐƚŚĂƚĂƌĞƉƌŽŚŝďŝƚĞĚďLJ
ŚŽŵĞŽǁŶĞƌƐ͘
ZĞƐƚƌŝĐƚŝŽŶƐŝĚĞŶƚŝĨŝĞĚŝŶ
ŵƉůŽLJĞĞDĂŶƵĂůĂŶĚ
ƌĞǀŝĞǁĞĚLJĞĂƌůLJďLJĞŵƉůŽLJĞĞƐ͘
zĞƐ
Eϯ͘ŽŵŵŽŶƌĞĂ>ĂŶĚƐĐĂƉĞĚDĂŶĂŐĞŵĞŶƚ
^ƉĞĐŝĨŝĐƉƌĂĐƚŝĐĞƐĂƌĞĨŽůůŽǁĞĚ͕ĂŶĚŽŶŐŽŝŶŐŵĂŝŶƚĞŶĂŶĐĞŝƐ ĐŽŶĚƵĐƚĞĚƚŽŵŝŶŝŵŝnjĞĞƌŽƐŝŽŶĂŶĚŽǀĞƌͲŝƌƌŝŐĂƚŝŽŶ͕ĐŽŶƐĞƌǀĞ ǁĂƚĞƌ͕ĂŶĚƌĞĚƵĐĞƉĞƐƚŝĐŝĚĞĂŶĚĨĞƌƚŝůŝnjĞƌĂƉƉůŝĐĂƚŝŽŶƐ͘ WƌŽĨĞƐƐŝŽŶĂůůĂŶĚƐĐĂƉĞĐŽŵƉĂŶLJƚŽĐŽŶĚƵĐƚ
ŵĂŝŶƚĞŶĂŶĐĞŽĨůĂŶĚƐĐĂƉŝŶŐƚŽŵĞĞƚĐƵƌƌĞŶƚ
ǁĂƚĞƌĞĨĨŝĐŝĞŶĐLJĂŶĚŬĞĞƉƉůĂŶƚƐŚĞĂůƚŚLJĂŶĚ
ďŝŽĂƌĞĂƐŵĂŝŶƚĂŝŶĞĚǁŝƚŚƉƌŽƉĞƌƐŽŝů
ĂŵĞŶĚŵĞŶƚƐ͘ZĞŐƵůĂƌŵĂŝŶƚĞŶĂŶĐĞŽŶĐĞĂ
ǁĞĞŬĂŶĚŵŽŶƚŚůLJŝŶƐƉĞĐƚŝŽŶƚŽĚĞƚĞƌŵŝŶĞ
ĚĞĨŝĐŝĞŶĐŝĞƐ
dŚĞ,KͬKtE
Zǁŝůů
ŵĂŝŶƚĂŝŶŽƌŚŝƌĞƉƌŽĨĞƐƐŝŽŶĂůƐ
ƚŽŵĂŶĂŐĞƚŚĞƵƉŬĞĞƉŽĨƚŚĞ
ƉƌŽũĞĐƚ͛ƐůĂŶĚƐĐĂƉĞĚĂƌĞĂƐ͘
zĞƐ
Eϰ͘DWDĂŝŶƚĞŶĂŶĐĞ
/ŶŽƌĚĞƌƚŽĞŶƐƵƌĞĂĚĞƋƵĂƚĞĂŶĚĐŽŵƉƌĞŚĞŶƐŝǀĞDW
ŝŵƉůĞŵĞŶƚĂƚŝŽŶ͕ĂůůƌĞƐƉŽŶƐŝďůĞƉĂƌƚŝĞƐĂƌĞŝĚĞŶƚŝĨŝĞĚĨŽƌ ŝŵƉůĞŵĞŶƚŝŶŐĂůůŶŽŶͲƐƚƌƵĐƚƵƌĂůĂŶĚƐƚƌƵĐƚƵƌĂůDWƐ͕ĐůĞĂŶŝŶŐ͕ ŝŶƐƉĞĐƚŝŽŶ͕ĂŶĚŽƚŚĞƌŵĂŝŶƚĞŶĂŶĐĞĂĐƚŝǀŝƚŝĞƐĂƌĞƐƉĞĐŝĨŝĞĚ ŝŶĐůƵĚŝŶŐƌĞƐƉŽŶƐŝďůĞƉĂƌƚŝĞƐĨŽƌĐŽŶĚƵĐƚŝŶŐƐƵĐŚĂĐƚŝǀŝƚŝĞƐ͘
ŵŝŶŝŵƵŵϮ/ŶƐƉĞĐƚŝŽŶƐͬůĞĂŶŝŶŐƐƉĞƌ
LJĞĂƌƉĞƌŵĂŶƵĨĂĐƚƵƌĞƌ͛ƐƐƉĞĐŝĨŝĐĂƚŝŽŶƐƉƌŝŽƌ
ƚŽKĐƚŽďĞƌϭ
Ɛƚ;ďĞĨŽƌĞƚŚĞƌĂŝŶLJƐĞĂƐŽŶͿ
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ZƚŽŚŝƌĞ
ƉƌŽĨĞƐƐŝŽŶĂůDWŵĂŝŶƚĞŶĂŶĐĞ
ĐŽŵƉĂŶLJƚŽĐŽŶĚƵĐƚƌĞŐƵůĂƌ
ŝŶƐƉĞĐƚŝŽŶƐ͕ƌĞƉĂŝƌƐ͕ĂŶĚ
ĐůĞĂŶŝŶŐƉĞƌŵĂŶƵĨĂĐƚƵƌĞƌ͛Ɛ
ƐƉĞĐŝĨŝĐĂƚŝŽŶƐ͘
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Eϱ͘dŝƚůĞϮϮZŽŵƉůŝĂŶĐĞ
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WĂŐĞϯŽĨϵ
ĂƐƐŽĐŝĂƚŝŽŶǁŝƚŚƚŚĞƉƌŽũĞĐƚ͖ŵĞĂƐƵƌĞƐĂƌĞƚĂŬĞŶƚŽĐŽŵƉůLJǁŝƚŚ ĂƉƉůŝĐĂďůĞůŽĐĂů͕ƐƚĂƚĞ͕ĂŶĚĨĞĚĞƌĂůƌĞŐƵůĂƚŝŽŶƚŽĂǀŽŝĚŚĂƌŵƚŽ ŚƵŵĂŶƐĂŶĚƚŚĞĞŶǀŝƌŽŶŵĞŶƚ͘
EŽ Eϳ͘^ƉŝůůŽŶƚŝŶŐĞŶĐLJWůĂŶ
EŽ Eϴ͘hŶĚĞƌŐƌŽƵŶĚ^ƚŽƌĂŐĞdĂŶŬŽŵƉůŝĂŶĐĞ
EK
EϭϬ͘hŶŝĨŽƌŵ&ŝƌĞŽĚĞ/ŵƉůĞŵĞŶƚĂƚŝŽŶ
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ZƚŽĐŽŵƉůLJǁŝƚŚĨŝƌĞƌĞŐƵůĂƚŝŽŶƐĂŶĚŬĞĞƉŝŶĨŽƌŵĞĚ
ŽĨƚŚĞůĂƚĞƐƚƌƵůĞƐĂŶĚƌĞƋƵŝƌĞŵĞŶƚƐ͘
ŽŵƉůLJǁŝƚŚĂŶŶƵĂůĨŝƌĞŝŶƐƉĞĐƚŝŽŶƐĂŶĚ
ŵĂŝŶƚĂŝŶďƵŝůĚŝŶŐĂŶĚĂĐĐĞƐƐƉĞƌƚŚĞůĂƚĞƐƚ
ĨŝƌĞĐŽĚĞƐ͘
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Eϭϭ͘ŽŵŵŽŶƌĞĂ>ŝƚƚĞƌŽŶƚƌŽů
dŚĞƉƌŽƉŽƐĞĚƉƌŽũĞĐƚǁŝůůŚĂǀĞǀĂƌŝŽƵƐƚƌĂƐŚƌĞĐĞƉƚĂĐůĞƐůŽĐĂƚĞĚ ŶĞĂƌƚŚĞĐŽŵŵŽŶĂƌĞĂƐ͘dƌĂƐŚŵĂŶĂŐĞŵĞŶƚĂŶĚůŝƚƚĞƌĐŽŶƚƌŽů ƉƌŽĐĞĚƵƌĞƐĂƌĞƐƉĞĐŝĨŝĞĚǁŝƚŚŝŶƚŚŝƐƌĞƉŽƌƚ͕ŝŶĐůƵĚŝŶŐ ƌĞƐƉŽŶƐŝďůĞƉĂƌƚŝĞƐ͕ĂŶĚŝŵƉůĞŵĞŶƚĞĚƚŽƌĞĚƵĐĞƉŽůůƵƚŝŽŶŽĨ ĚƌĂŝŶĂŐĞǁĂƚĞƌ͘
KŶĐĞƉĞƌǁĞĞŬƉƌŽǀŝĚĞůŝƚƚĞƌƌĞŵŽǀĂůŽĨƐŝƚĞ
ƉĂƌŬŝŶŐůŽƚĂŶĚůĂŶĚƐĐĂƉĞĂƌĞĂƐĂŶĚƚŽ
ĞŵƉƚLJĐŽŵŵŽŶĂƌĞĂƚƌĂƐŚďŝŶƐ͘
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EϭϮ͘
ŵƉůŽLJĞĞdƌĂŝŶŝŶŐ
WƌĂĐƚŝĐĂůŝŶĨŽƌŵĂƚŝŽŶĂůŵĂƚĞƌŝĂůƐĂŶĚͬŽƌƚƌĂŝŶŝŶŐĂƌĞƉƌŽǀŝĚĞĚƚŽ ĞŵƉůŽLJĞĞƐĂƚƚŚĞŝŶŝƚŝĂůƚŝŵĞŽĨŚŝƌŝŶŐďLJƚŚĞ,KͬKtE ZƚŽ
ŝŶĐƌĞĂƐĞƚŚĞŝƌƵŶĚĞƌƐƚĂŶĚŝŶŐŽĨƐƚŽƌŵǁĂƚĞƌƋƵĂůŝƚLJ͕ƐŽƵƌĐĞƐŽĨ ƉŽůůƵƚĂŶƚƐ͕ĂŶĚƚŚĞŝƌƌĞƐƉŽŶƐŝďŝůŝƚLJĨŽƌƌĞĚƵĐŝŶŐƉŽůůƵƚĂŶƚƐŝŶ ƐƚŽƌŵǁĂƚĞƌ͘
dŚĞĚŝƐƚƌŝďƵƚŝŽŶŽĨƚŚĞƐĞŵĂƚĞƌŝĂůƐǁŝůůďĞ
ƚŚĞƌĞƐƉŽŶƐŝďŝůŝƚLJŽĨƚŚĞ,KͬKtE
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ŝŶŝƚŝĂůŚŝƌŝŶŐŽĨƚŚĞĞŵƉůŽLJĞĞ͘
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Eϭϰ͘ŽŵŵŽŶƌĞĂĂƚĐŚĂƐŝŶ/ŶƐƉĞĐƚŝŽŶ
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ŝŵƉůĞŵĞŶƚĂƚŝŽŶ͕ĂůůƌĞƐƉŽŶƐŝďůĞƉĂƌƚŝĞƐĂƌĞŝĚĞŶƚŝĨŝĞĚĨŽƌ ŝŵƉůĞŵĞŶƚŝŶŐĂůůŶŽŶͲƐƚƌƵĐƚƵƌĂůĂŶĚƐƚƌƵĐƚƵƌĂůDWƐ͕ĐůĞĂŶŝŶŐ͕ ŝŶƐƉĞĐƚŝŽŶ͕ĂŶĚŽƚŚĞƌŵĂŝŶƚĞŶĂŶĐĞĂĐƚŝǀŝƚŝĞƐĂƌĞƐƉĞĐŝĨŝĞĚ ŝŶĐůƵĚŝŶŐƌĞƐƉŽŶƐŝďůĞƉĂƌƚŝĞƐĨŽƌĐŽŶĚƵĐƚŝŶŐƐƵĐŚĂĐƚŝǀŝƚŝĞƐ͘ /ŶƐƉĞĐƚŝŽŶƚǁŝĐĞƉĞƌŵŽŶƚŚŽĨĐŽŵŵŽŶ
ĂƌĞĂƐǁŚĞƌĞĐĂƚĐŚďĂƐŝŶƐĂƌĞůŽĐĂƚĞĚǁŝƚŚŝŶ
ƚŚĞƐƵƌƌŽƵŶĚŝŶŐĂƌĞĂĂŶĚƌĞŵŽǀĞĂŶLJƚƌĂƐŚͬ
ĚĞďƌŝƐ͘
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Eϭϱ͘^ƚƌĞĞƚ^ǁĞĞƉŝŶŐWƌŝǀĂƚĞ^ƚƌĞĞƚƐĂŶĚWĂƌŬŝŶŐ>ŽƚƐ
ZĞŐƵůĂƌƐǁĞĞƉŝŶŐŝƐĐŽŶĚƵĐƚĞĚƚŽƌĞĚƵĐĞƉŽůůƵƚŝŽŶŽĨĚƌĂŝŶĂŐĞ ǁĂƚĞƌ͘
ŝƚLJ͛Ɛ^ƚƌĞĞƚ^ǁĞĞƉŝŶŐ^ĞƌǀŝĐĞƐŽƌĂƉƉƌŽǀĞĚ
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EĂŵĞŽĨdƌĂŝŶĞĞ ĂƚĞ
WĂŐĞϵŽĨϵ
GENERAL SPECIFICATIONS FOR MAINTENANCE OF
FLO-GARDTM+PLUS CATCH BASIN INSERT FILTERS
SCOPE:
Federal, State and Local Clean Water Act regulations and those of insurance carriers require that stormwater filtration systems be maintained and serviced on a recurring basis. The intent of the regulations is to ensure that the systems, on a continuing basis, efficiently remove pollutants from stormwater runoff thereby preventing pollution of the nation’s water resources. These Specifications apply to the Flo-Gard TM
+Plus Catch Basin Insert Filter.
RECOMMENDED FREQUENCY OF SERVICE:
Drainage Protection Systems (DPS) recommends that installed Flo-GardTM +Plus Catch Basin Insert Filters be serviced on a recurring basis. Ultimately, the frequency depends on the amount of runoff, pollutant loading and interference from debris (leaves, vegetation, cans, paper, etc.); however, it is recommended that each installation be serviced a minimum of three times per year, with a change of filter medium once per year. DPS technicians are available to do an on-site evaluation, upon request.
RECOMMENDED TIMING OF SERVICE:
DPS guidelines for the timing of service are as follows:
1. For areas with a definite rainy season: Prior to, during and following the rainy season.
2. For areas subject to year-round rainfall: On a recurring basis (at least three times per year).
3. For areas with winter snow and summer rain: Prior to and just after the snow season and during the summer rain season.
4. For installed devices not subject to the elements (washracks, parking garages, etc.): On a recurring basis (no less than three times per year).
SERVICE PROCEDURES:
1. The service shall commence with collection and removal of sediment and debris (litter, leaves, papers, cans, etc.) and broom sweeping around the drainage inlet. Accumulated materials shall be placed in a DOT approved container for later disposal.
2. The catch basin shall be visually inspected for defects and possible illegal dumping. If illegal dumping has occurred, the proper authorities and property owner representative shall be notified as soon as practicable.
3. The catch basin grate shall be removed and set to one side. Using an industrial vacuum, the collected materials shall be removed from the liner. (Note: DPS uses a truck-mounted vacuum for servicing Flo-Gard
TM +Plus catch basin inserts.)
4. When all of the collected materials have been removed, the filter medium pouches shall be removed by unsnapping the tether from the D-ring and set to one side. The filter liner, gaskets, stainless steel frame and mounting brackets, etc. shall be inspected for continued serviceability.
Minor damage or defects found shall be corrected on-the-spot and a notation made on the Maintenance Record. More extensive deficiencies that affect the efficiency of the filter (torn liner, etc.), if approved by the customer representative, will be corrected and an invoice submitted to the representative along with the Maintenance Record.
5. The filter medium pouches shall be inspected for defects and continued serviceability and replaced as necessary and the pouch tethers re-attached to the liner’s D-ring. See below.
6. The grate shall be replaced.
EXCHANGE AND DISPOSAL OF EXPOSED FILTER MEDIUM AND COLLECTED DEBRIS The frequency of filter medium pouch exchange will be in accordance with the existing DPS-Customer Maintenance Contract. DPS recommends that the medium be changed at least once per year. During the appropriate service, or if so determined by the service technician during a non-scheduled service, the filter medium pouches will be replaced with new pouches and the exposed pouches placed in the DOT approved container, along with the exposed debris. Once the exposed pouches and debris have been placed in the container, DPS has possession and must dispose of it in accordance with local, state and federal agency requirements.
Note: As the generator, the landowner is ultimately responsible for the proper disposal of the exposed filter medium and debris. Because the materials likely contain petroleum hydrocarbons, heavy metals and other harmful pollutants, the materials must be treated as an EPA Class 2 Hazardous Waste and properly disposed of. DPS relieves the landowner of the actual disposal task, and provides certification of its completion in accordance with appropriate regulations.
DPS also has the capability of servicing all manner of catch basin inserts and catch basins without inserts, underground oil/water separators, stormwater interceptors and other such devices. All DPS personnel are highly qualified technicians and are confined space trained and certified. Call us at (888) 950-8826 for further information and assistance.
05/04/04
MAINTENANCE, INSPECTION, AND REPAIR LOG
Site: 18616 Rorimer Street, La Puente Page: of
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Inspection and Maintenance Guide
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SCOPE:
Federal, State and Local Clean Water Act regulations and those of insurance carriers require that stormwater filtration systems be maintained and serviced on a recurring basis. The intent of the regulations is to ensure that the systems, on a continuing basis, efficiently remove pollutants from stormwater runoff thereby preventing pollution of the nation’s water resources. These specifications apply to the FloGard+Plus® Catch Basin Insert Filter.
RECOMMENDED FREQUENCY OF SERVICE:
Drainage Protection Systems (DPS) recommends that installed FloGard+Plus Catch Basin Insert Filters be serviced on a recurring basis. Ultimately, the frequency depends on the amount of runoff, pollutant loading and interference from debris (leaves, vegetation, cans, paper, etc.); however, it is recommended that each installation be serviced a minimum of three times per year, with a change of filter medium once per year. DPS technicians are available to do an onsite evaluation, upon request.
RECOMMENDED TIMING OF SERVICE:
DPS guidelines for the timing of service are as follows:
1. For areas with a definite rainy season: Prior to, during and following the rainy season.
2. For areas subject to year-round rainfall: On a recurring basis (at least three times per year).
3. For areas with winter snow and summer rain: Prior to and just after the snow season and during the summer rain season.
4. For installed devices not subject to the elements (washracks, parking garages, etc.): On a recurring basis (no less than three times per year).
SERVICE PROCEDURES:
1. The catch basin grate shall be removed and set to one side. The catch basin shall be visually inspected for defects and possible illegal dumping. If illegal dumping has occurred, the proper authorities and property owner representative shall be notified as soon as practicable.
2. Using an industrial vacuum, the collected materials shall be removed from the liner. (Note: DPS uses a truck-mounted vacuum for servicing FloGard+Plus catch basin inserts.)
3. When all of the collected materials have been removed, the filter medium pouches shall be removed by unsnapping the tether from the D-ring and set to one side. The filter liner, gaskets, stainless steel frame and mounting brackets, etc., shall be inspected for continued serviceability. Minor damage or defects found shall be corrected on-the-spot and a notation made on the Maintenance Record.
More extensive deficiencies that affect the efficiency of the filter (torn liner, etc.), if approved by the customer representative, will be corrected and an invoice submitted to the representative along with the Maintenance Record.
4. The filter medium pouches shall be inspected for defects and continued serviceability and replaced as necessary and the pouch tethers re-attached to the liner’s D-ring. See below.
5. The grate shall be replaced.
REPLACEMENT AND DISPOSAL OF EXPOSED FILTER MEDIUM AND COLLECTED DEBRIS The frequency of filter medium exchange will be in accordance with the existing DPS-Customer Maintenance Contract. DPS recommends that the medium be changed at least once per year. During the appropriate service, or if so determined by the service technician during a non-scheduled service, the filter medium will be replaced with new material. Once the exposed pouches and debris have been removed, DPS has possession and must dispose of it in accordance with local, state and federal agency requirements.
DPS also has the capability of servicing all manner of storm drain filters, catch basin inserts and catch basins without inserts, underground oil/water separators, stormwater interceptors and other such devices.
All DPS personnel are highly qualified technicians and are confined space trained and certified. Call us at (888) 950-8826 for further information and assistance.
2 www.oldcastlestormwater.com
800-579-8819
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131 Calle Iglesia, Suite 200, San Clemente, CA 92672 (949) 369-6141 www.lgcgeotechnical.com June 26, 2025 Project No. 25041-01
Mr. Matthew J. Waken
Crestfield Townhomes, LLC
27702 Crown Valley Parkway, Suite D-4-197
Ladera Ranch, CA 92694
Subject: Preliminary Geotechnical Evaluati on and Recommendations, Proposed Residential Development, Located at 225 Colorado Pl ace (Motel 6) and 201 Colorado Place, Arcadia, County of Los Angeles, California
In accordance with your request and authorization, LGC Geotechnical, Inc. has performed a preliminary geotechnical evaluation for the proposed residential development, located at 225 Colorado Place (Motel 6) and 201 Colorado Place in the City of Arcadia, County of Los Angeles, California. The purpose of our study was to evaluate the existing onsite geotec hnical conditions and to provide geotechnical recommendations relative to the proposed residential development.
Should you have any questions regarding this report, please do not hesitate to contact our office. We appreciate this opportunity to be of service.
Respectfully Submitted,
LGC Geotechnical, Inc.
Ryan Douglas, PE, GE 3147 Mason Gonzales, PG 10174
Vice President of Engineering Project Geologist
John Navarrete
Senior Staff Engineer
RLD/JMN/amm
Distribution: (1) Addressee (electronic copy)
Project No. 25041-01 Page i June 26, 2025
TABLE OF CONTENTS
Section Page
1.0 INTRODUCTION ...................................................................................................................................... 1
1.1 Purpose and Scope of Services ............................................................................................. .............. 1
1.2 Project Description ....................................................................................................... .......................... 1
1.3 Subsurface Geotec hnical Evaluation ........................................................................................ ....... 3
1.4 Field Infiltration Testing ................................................................................................ ...................... 3
1.5 Laboratory Testing ........................................................................................................ ......................... 4
2.0 GEOTECHNICAL CONDITIONS ............................................................................................................. 6
2.1 Regional Geology .......................................................................................................... ........................... 6
2.2 Site-Specific Geology and Generalized Subsurface Conditions ............................................... 6
2.3 Groundwater ............................................................................................................... .............................. 7
2.4 Seismic Desi gn Criteria ................................................................................................... ...................... 7
2.5 Faulting .................................................................................................................. ..................................... 8
2.5.1 Liquefaction and Dynamic Settlement .............................................................................. 9
2.5.2 Lateral Spreading ....................................................................................................... ............. 10
2.6 Oversized Material ........................................................................................................ ........................ 10
2.7 Expansion Potential ....................................................................................................... ....................... 10
3.0 CONCLUSIONS ........................................................................................................................................ 11
4.0 PRELIMINARY RECOMMENDATIONS ............................................................................................ 12
4.1 Site Earthwork ............................................................................................................ ........................... 12
4.1.1 Site Preparation ........................................................................................................ ............... 12
4.1.2 Removal and Recompaction Depths and Limits .......................................................... 13
4.1.3 Temporary Excavations ................................................................................................... .... 14
4.1.4 Removal Bottoms and Subgrade Preparation .............................................................. 15
4.1.5 Material for Fill ....................................................................................................... ................. 15
4.1.6 Placement and Compaction of Fills ................................................................................... 16
4.1.7 Trench and Retaining Wall Backfill and Compaction ................................................. 16
4.1.8 Shrinkage an d Subsidence ................................................................................................ .. 17
4.2 Preliminary Foundation Recommendations ............................................................................... 18
4.2.1 Provisional Conventional Foun dation Design Parameters .................................... 18
4.2.2 Provisional Post-Tensioned Fo undation Design Parameters ............................... 18
4.2.3 Post-Tensioned Foundation Subgra de Preparation and Maintenance ............. 18
4.2.4 Slab Underlayme nt Guidelines .......................................................................................... 19
4.3 Soil Bearing and Lateral Resistance ....................................................................................... ....... 20
4.4 Lateral Earth Pressure s for Retaining Walls .............................................................................. 20
4.5 Control of Surface Water and Drainage Control ......................................................................... 22
4.6 Subsurface Water Infiltration ............................................................................................. .............. 23
4.7 Preliminary Asphal t Pavement Sections .................................................................................... 25
4.8 Soil Corrosivity .......................................................................................................... ............................. 26
4.9 Nonstructural Concrete Flatwork ........................................................................................... ........ 27
4.10 Geotechnical Plan Review ................................................................................................. ................. 28 TABLE OF CONTENTS (Cont’d)
Project No. 25041-01 Page ii June 26, 2025
4.11 Geotechnical Observation and Testing During Construction ................................................ 28
5.0 LIMITATIONS ......................................................................................................................................... 29
LIST OF ILLUSTRATIONS, TABLES, AND APPENDICES
Figures
Figure 1 – Site Location Map (Page 2)
Figure 2 – Boring Location Map (Rear of Text)
Figure 3 – Retaining Wall Backfill Detail (Rear of Text)
Tables
Table 1 – Summary of Field Infiltration Testing (Page 4) Table 2 – Seismic Design Parameters (Page 8)
Table 3 – Lateral Earth Pressures – Approved Onsite or Imported Sandy Soils (Page 21) Table 4 – Shallow Surface Infiltration - Reduction Factors Applied to Infiltration Rate (Page 24)
Table 5 – Preliminary Pavement Sections (Page 25)
Table 6 – Nonstructural Concrete Flatwork Guidelines for Very Low Expansion Potential (Page 27)
Appendices
Appendix A – References
Appendix B – Boring Logs
Appendix C – Laboratory Test Results
Appendix D – Infiltration Test Results
Appendix E – General Earthwork and Grading Specifications for Rough Grading
Project No. 25041-01 Page 1 June 26, 2025
1.0 INTRODUCTION
1.1 Purpose and Scope of Services
This report presents the results of our prelim inary geotechnical evaluation for the proposed residential development, located at 225 and 201 Colorado Place in the City of Arcadia, County of Los Angeles, California. Refer to the Site Location Map (Figure 1).
The purpose of our study was to provide a geotechnical evaluation relative to the proposed residential development. As part of our scope of work, we have: 1) reviewed available geotechnical information and in-house geologic maps pertinent to the site (Appendix A); 2) performed a subsurface geotechnical evaluation of the site consisting of the excavation and sampling of eight small-diameter borings ranging from approximately 10.0 to 50.5 feet below existing ground surface, 3) performed four fallin g head infiltration tests within the borings; 4) performed laboratory testing of select soil samples obtained du ring our subsurface evaluation; and 5) prepared this preliminary geotechnical summary report presenting our findings and preliminary conclusions and recommendations for the development of the proposed project.
It should be noted that our evaluation and this report only address geotechnical issues associated with the site and do not address any environmental issues.
1.2 Project Description
The approximately 3.7-acre site is bound to the north by Barnhart School and west by Colorado P l a c e , t o t h e e a s t b y e x i s t i n g r e s i d e n t i a l h o m e s an d t o t h e s o u t h b y S a n J u a n D r i v e . T h e s i t e i s currently occupied by a Motel 6 on the nort hern portion and the California Thoroughbred Breeders Association building on the southern portion.
The site is bisected by an open U-shaped channel (wash) which runs north to south along the east side of the Motel 6 parcel leading into an underground culvert that spits the Motel 6 parcel and Thoroughbred parcel in the southern portion of the overall site. The exact dimensions and details of the channel and culvert are unknown at this time and the agency that owns the channel and culvert may have specific guidelines for lo ading and setback from the improvements. The proposed improvements relative to the existing channel and culvert should be further reviewed when grading plans are further developed and the details regarding the channel/culvert are available for review.
The proposed development consists of 86 multi-fa mily residential units, internal drive alleys, open space and other associated improvements. Design cut and fill information is not available at this time but is expected to be on the order of less than 2 to 3 feet. The proposed residential development is anticipated to consist of relatively light building loads (column and wall loads maximum of 20 kips and 2 kips per linear foot, respectively).
The recommendations given in this report are based upon at-grade structures with estimated structural loads and grading information indicated above. LGC Geotechnical should be provided with any updated project information, plans and/or any structural loads when they become available, in order to either confirm or modify the recommendations provided herein. 6LWH/RFDWLRQ
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Project No. 25041-01 Page 3 June 26, 2025
1.3 Subsurface Geotechnical Evaluation
A limited subsurface geotechnical evaluation of the site was performed by LGC Geotechnical. Our exploration program consisted of drilling and sampling eight small-diameter exploratory hollow- stem borings (HS-1 through HS-4 and I-1 through I-4) for the purpose of obtaining samples for evaluation and laboratory testing of site soils and performing infiltration testing.
The borings were drilled by Choice Drilling under subcontract to LGC Geotechnical. The depths of the borings ranged from approximately 10.0 to 50.5 feet below existing grade. An LGC Geotechnical representative observed the drilling operations, lo gged the borings, and collected soil samples for laboratory testing. The borings were performed using a truck-mounted drill rig equipped with 8-inch-diameter hollow-stem augers. Bulk samples of the near-surface soils were logged and collected for laboratory testing from select borings. Driven soil samples were collected by means of the Standard Penetration Test (SPT) and Modified California Drive (MCD) sampler generally obtained at 2.5 and 5-foot ve rtical increments. The MCD is a split-barrel sampler with a tapered cutting tip and lined with a s e r i e s o f 1 - i n c h - t all brass rings. The SPT sampler (1.4-inch ID) and MCD sampler (2.4-inch ID, 3.0-inch OD) were driven using a 140- pound automatic hammer falling 30 inches to advance the sampler a total depth of 18 inches or until refusal. The raw blow counts for each 6-inch increment of penetration were recorded on the boring logs. The borings were subsequently backfilled with soil cuttings and tamped and capped with asphalt cold patch. Some settlement of the backfill soils may occur over time.
Infiltration testing was performed within the four borings (I-1 through I-4) to depths of approximately 10 to 15 feet below existing gr ade. An LGC Geotechnical engineer installed standpipes, backfilled the borings with crushed rock and pre-soaked the infiltration holes prior to testing. Infiltration testing was performed per the County of Los Angeles testing guidelines (2021). Standpipes were removed and the location s were subsequently backfilled with native soils at the completion of testing. Some settlement of the backfill soils may occur over time.
The approximate locations of our subsurface expl orations are provided on the Boring Location Map (Figure 2). The boring logs are provided in Appendix B.
1.4 Field Infiltration Testing
Four shallow infiltration test wells were inst alled in Borings I-1 through I-4 to approximate depths of 10 to 15 feet below existing grade. Th e approximate infiltration boring locations are shown on the Boring Location Map (Figure 2). Estimation of infiltration rates was performed in general accordance with the “Boring Percolation Test Procedure” guidelines set forth by the County of Los Angeles testing guidelines (2021). The borings for the infiltration tests were excavated using a drill rig equipped with 8-in ch diameter hollow-stem augers. A 3-inch diameter perforated PVC pipe was placed in the borehole above a thin layer of gravel and the annulus was backfilled wi th gravel. Infiltration tests were performed using relatively clean water free of particulates, silt, etc. The infiltration wells were pre-soaked during the day of drilling and a 30-minute pre-test was performe d during the day of testing. Subsequently, readings were taken a minimum of 6 times or until a “stabilized rate” was established. A “stabilized rate” is when the highest and lowest readings are within 10 percent of each other over three consecutive readings. At the completion of infiltration testing, the pipe was removed, and the holes were backfilled and tamped.
Project No. 25041-01 Page 4 June 26, 2025
Based on the County of Los Angeles testing guidelines (2021), the infiltration rate is calculated by dividing the volume of water discharged by the surface area of the test section (including the sidewalls and bottom of the boring) over a specific time period. The infiltration rate is taken as the average of the last three readings during which a “stabilized rate” is achieved. The infiltration rates are provided in Table 1 below.
TABLE 1
Summary of Field Infiltration Testing
Infiltration Test
Location
Approximate
Infiltration Test
Depth (ft)
Infiltration Rate*
(inch/hr.)
I-1 10.0 0.7
I-2 15.0 6.9
I-3 15.0 5.3
I-4 10.0 4.4
*Does Not Include Required Reduction Factors for Design.
Please note that the values provided in Table 1 do not include reduction factors associated with the test procedure, site variability, and long-ter m siltation plugging that are used to calculate the design infiltration rate. Infiltration test data is presented in Appendix D. Refer to Section 4.6 for recommendations regarding infiltration of stormwater.
1.5 Laboratory Testing
Representative bulk, grab, and driven (relatively undisturbed) samples were retained for laboratory testing during our field evaluation. Laboratory testing included in-situ moisture content and in-situ dry density, expansion index, fines content, Atterberg limits, consolidation, direct shear, laboratory compaction, and corrosion (sulfate, chloride, pH and minimum resistivity).
The following is a summary of the laboratory test results:
x Dry density of the samples collected ranged from approximately 99 pounds per cubic foot (pcf) to 119 pcf, with an average of 110 pcf. Field moisture contents ranged from approximately 2 to 14 percent, with an average of approximately 7 percent. x Two Expansion Index (EI) tests was performed. The results indicate an EI value of 1, corresponding to “Very Low” expansion potential.
x Three samples were tested for fines content indicating a fines content (passing No. 200 sieve) ranging from 4 to 38 percent. Accordin g to the Unified Soils Classification System (USCS), the tested samples are classified as “coarse grained” soil. x Two Atterberg Limit (liquid limit and plastic li mit) test was performed. Results indicated a Plasticity Index (PI) range of 4 to 7.
x Two consolidation tests were performed. The deformation versus vertical stress plots are provided in Appendix C.
Project No. 25041-01 Page 5 June 26, 2025
x Two direct shear test was performed. The plots are provided in Appendix C. x Laboratory compaction of a near-surface bulk sample resulted in a maximum dry density of 130.5 pcf at an optimum moisture content of 8.5 percent. x Corrosion testing indicated soluble sulfate cont ent of less than 0.01 percent, a chloride content ranging from 28 to 29 parts per million (ppm), pH ranging from 7.4 to 7.6 and a minimum resistivity ranging from 13,400 to 15,410 ohm-centimeters.
A summary of the laboratory test results is presented in Appendix C. The moisture and dry density results are presented on the boring logs in Appendix B.
Project No. 25041-01 Page 6 June 26, 2025
2.0 GEOTECHNICAL CONDITIONS
2.1 Regional Geology
The site is located south of the foothills belo w the San Gabriel Mountains in the northern San Gabriel Valley within the transition area of Ca lifornia’s Peninsular and Transverse geomorphic provinces. The Peninsular Ranges are characterized by northwest trending mountain ranges, generally dominated by right lateral strike-slip faulting. The Transverse Ranges are characterized by predominately east-west trending mountain ranges dominated by reverse faulting. The Transverse Ranges geomorphology can be generally be attributed to the effects of the major bend within the northwest trending San Andreas faul t and the subsequent north-south compression that results. The San Gabriel Mountain Range rises steeply north of the site and provides the sediment source for the alluvial fan deposits that underlie the area of the subject site (CGS, 2018).
The site is within the San Gabriel Valley, west of the Santa Anita Wash (Dibblee, et al, 1998).
The subject area is more locally geologically bounded at the north by the Raymond Fault (approximately 700 feet north of the site) and the Sierra Madre Fault Zone (approximately 2 miles north of the site). The Sierra Madre Fault Zone consists of reverse faults dipping to the north. The northeast trending Raymond Fault joins the east west trending Sierra Madre Fault Zone approximately 3 miles to the northeast of the site. The Raymond Fault is a left lateral fault that is generally assumed to be a part of the San Andreas Fault system.
2.2 Site-Specific Geology and Generalized Subsurface Conditions
Based on review of the available geologic map (Dibblee, et al, 1998), the primary geologic unit underlying the site is Quaternary alluvial depo sits. The undissected fan is largely described as alluvial gravel, sand, and silt (Dibblee, et al, 1998).
The field explorations (borings) indicate the nati ve alluvial soils generally consist of variable amounts of clayey sand, silty sand, and sand ra nging from brown to gray, dry to moist, and generally medium dense/medium stiff to very dense/very stiff to the maximum explored depth o f a p p r o x i m a t e l y 5 0 . 5 f e e t b e l o w e x i s t i n g g r a d e . P o t e n t i a l l y u p t o f i v e f e e t o f u n d o c u m e n t e d artificial fill may be present across the site but was not differentiated on the boring logs. Deeper amounts of undocumented fill, not encountered in the borings, may exist locally beneath the current building footprints and in various other areas across the site. These materials should be removed to competent native materials prior to placement of compacted fill.
It should be noted that borings are only representative of the location and time where/when they are performed and varying subsurface conditions may exist outside of the performed location. In addition, subsurface conditions can change over time. The soil descriptions provided above should not be construed to mean that the subs urface profile is uniform, and that soil is homogeneous within the project area. For details on the stratigraphy at the exploration locations, refer to Appendix B.
Project No. 25041-01 Page 7 June 26, 2025
2.3 Groundwater
Groundwater was not encountered to the maxi mum depth of approximately 50.5 feet below existing ground surface during our subsurface ev aluation. Historic high groundwater is greater than 100 feet below current grade per the Seis m i c H a z a r d R e p o r t o f t h e M o u n t W i l s o n 7 . 5 - Minute Quadrangle, (CDMG, 1998). Groundwater is not expected to impact the proposed development.
Seasonal fluctuations of groundwater elevations should be expected over time. In general, groundwater levels fluctuate with the seasons and local zones of perched groundwater may be present due to local seepage caused by irrigati on and/or recent precipitation. Local perched groundwater conditions or surface seepage may develop once site development is completed.
2.4 Seismic Design Criteria
The site seismic characteristics were evaluated per the guidelines set forth in Chapter 16, Section 1613 of the 2022 California Building Code (CBC) and applicable portions of ASCE 7-16 which has been adopted by the CBC. Please note that the following seismic parameters are only applicable for code-based acceleration response spectra and are not applicable for where site-specific ground motion procedures are required by ASCE 7-16. Representative site coordinates of latitu de 34.143305 degrees north and lo ngitude -118.039915 degrees west were utilized in our analyses. The maximum co nsidered earthquake (MCE) spectral response accelerations (SMS and SM1) and adjusted design spectral response acceleration parameters (S DS and SD1) for Site Class D are provided in Table 2 on the following page. Since site soils are Site Class D, additional adjustments are required to code acceleration response spectrums as outlined below and provided in ASCE 7-16. The structural designer should contact the geotechnical consultant if structural conditions (e.g., number of stories, seismically isolated structures, etc.) require site-specific ground motions.
A deaggregation of the PGA based on a 2,475-year average return period (MCE) indicates that an earthquake magnitude of 7.05 at a distance of 8.76 km from the site would contribute the most to this ground motion. A deaggregation of the PGA based on a 475-year average return period (Design Earthquake) indicates that an earthquake magnitude of 6.96 at a distance of
13.79 km from the site would contribute the most to this ground motion (USGS, 2014).
Section 1803.5.12 of the 2022 CBC (per Section 11.8.3 of ASCE 7) states that the maximum considered earthquake geometric mean (MCE G) Peak Ground Acceleration (PGA) should be used for liquefaction potential. The PGA M for the site is equal to 0.958g (SEAOC, 2025). The design PGA is equal to 0.639g (2/3 of PGAM).
Project No. 25041-01 Page 8 June 26, 2025
TABLE 2
Seismic Design Parameters
Selected Parameters from 2022 CBC,
Section 1613 - Earthquake Loads
Seismic
Design
Values
Notes/Exceptions
Distance to applicable faults classifies the site as a
“Near-Fault” site. Section 11.4.1 of ASCE 7
Site Class D* Chapter 20 of ASCE 7
Ss (Risk-Targeted Spectral Acceleration
for Short Periods) 2.000g From SEAOC, 2025
S1 (Risk-Targeted Spectral
Accelerations for 1-Second Periods) 0.736g From SEAOC, 2025 Fa (per Table 1613.2.3(1)) 1.000
For Simplified Design Procedure
of Section 12.14 of ASCE 7, Fa
shall be taken as 1.4 (Section
12.14.8.1)
Fv (per Table 1613.2.3(2)) 1.700
Value is only applicable per
requirements/exceptions per
Section 11.4.8 of ASCE 7
SMS for Site Class D
[Note: SMS = FaSS] 2.000g -
SM1 for Site Class D
[Note: SM1 = FvS1] 1.251g
Value is only applicable per
requirements/exceptions per
Section 11.4.8 of ASCE 7
SDS for Site Class D
[Note: SDS = (2/3)SMS] 1.333g -
SD1 for Site Class D
[Note: SD1 = (2/3)SM1] 0.834g
Value is only applicable per
requirements/exceptions per
Section 11.4.8 of ASCE 7
CRS (Mapped Risk Coefficient at 0.2 sec) 0.888 ASCE 7 Chapter 22 CR1 (Mapped Risk Coefficient at 1 sec) 0.891 ASCE 7 Chapter 22 *Since site soils are Site Class D and S 1 is greater than or equal to 0.2, the seismic response coefficient Cs is determined by Eq. 12.8-2 for value ζ ͳ Ǥ ͷ s and taken equal to 1.5 times the value calculated in accordance with either Eq. 12.8-3 for T L ηεs, or Eq. 12.8-4 εL. Refer to ASCE 7-16.
2.5 Faulting
P r o m p t e d b y d a m a g i n g e a r t h q u a k e s i n N o r t h e r n and Southern California, State legislation and policies concerning the classification and land-u se criteria associated with faults have been developed. Their purpose was to prevent the co nstruction of urban developments across the t r a c e o f a c t i v e f a u l t s , r e s u l t i n g i n t h e A l q u i s t - P r i o l o E a r t h q u a k e F a u l t Z o n i n g A c t . E a r t h q u a k e Fault Zones have been delineated along the traces of active faults within California. Where developments for human occupation are proposed within these zones, the state requires detailed
Project No. 25041-01 Page 9 June 26, 2025
fault evaluations be performed so that engineering geologists can mitigate the hazards associated with active faulting by identifying the location of active faults and allowing for a setback from the zone of previous ground rupture.
T h e s u b j e c t s i t e i s n o t l o c a t e d w i t h i n a S t a t e o f C a l i f o r n i a E a r t h q u a k e F a u l t Z o n e ( A l q u i s t - Priolo) and no active faults are identified on the site (CGS, 2025). The possibility of damage due to ground rupture is considered low since no active faults are known to cross the site.
Secondary effects of seismic shaking resulting from large earthquakes on the major faults in the Southern California region, which may affect the site, include ground lurching and shallow ground rupture, soil liquefaction, and dynamic settlement. These secondary effects of seismic shaking are a possibility throughout the Southern California region and are dependent on the distance between the site and causative fault and the onsite geology. The closest major active faults that could produce these secondary effe cts include the Sierra Madre, Raymond, San Andreas, and Puente Hills Faults, among others. A discussion of these secondary effects is provided in the following sections.
2.5.1 Liquefaction and Dynamic Settlement
Liquefaction is a seismic phen omenon in which loose, saturated, granular soils behave similarly to a fluid when subject to high-intensity ground shaking. Liquefaction occurs when three general conditions coexist: 1) shallow groundwater; 2) low density non- cohesive (granular) soils; and 3) high-intensity ground motion. Studies indicate that saturated, loose near-surface cohesionless soils exhibit the highest liquefaction potential, while dry, dense, cohesionless soils and cohesive soils exhibit low to negligible liquefaction potential. In general, cohesi ve soils are not considered susceptible to liquefaction, depending on their plasticity and moisture content (Bray & Sancio, 2006).
Effects of liquefaction on level ground include settlement, sand boils, and bearing capacity failures below structures. Dynamic settlement of dry loose sands can occur as the sand particles tend to settle and densify as a result of a seismic event.
Based on our review of the State of California Department of Conservation, Earthquake Zones of Required Investigation (CGS, 2025), the subject site is not within a liquefaction hazard zone. Based on our evaluation, site soils are generally not susceptible to liquefaction due to the lack of a static groundwater table within the upper 50 feet and relatively dense on-site soils. However isolat ed sand layers may be susceptible to dry sand seismic settlement. Seismically induce d dry sand settlement s were estimated by the procedures outlined by Pradel (Pradel, 1998) and utilizing the design earthquake parameters. Based on the data obtained from our field evaluation, seismic settlement due to dry sands is estimated to be on the order of about 0.5-inches. Differential seismic settlement may be estimated as one-half of the total settlement over a horizontal span of 40 feet (e.g., 0.25-inch over a horizontal span of 40 feet).
Project No. 25041-01 Page 10 June 26, 2025
2.5.2 Lateral Spreading
Lateral spreading is a type of liquefaction-i nduced ground failure associated with the lateral displacement of surficial blocks of sediment resulting from liquefaction in a s u b s u r f a c e l a y e r . O n c e l i q u e f a c t i o n t r a n s f o r m s t h e s u b s u r f a c e l a y e r i n t o a f l u i d m a s s , gravity plus the earthquake inertial forc es may cause the mass to move downslope towards a free face (such as a river channel or an embankment). Lateral spreading may cause large horizontal displacements and su ch movement typically damages pipelines, utilities, bridges, and structures.
D u e t o t h e l a c k o f g r o u n d w a t e r i n t h e u p p e r 5 0 f e e t , a n d v e r y l o w p o t e n t i a l f o r liquefaction, the potential for lateral spreading is considered very low.
2.6 Oversized Material
Oversized materials (material larger than 8 inches in maximum dimension) may be encountered during site grading based on ou r subsurface evaluation. If encountered, recommendations are provided for appropriate handling of oversized materials in Appendix E.
2.7 Expansion Potential
Based on the results of our laboratory testing, site soils are anticipated to have a “Very Low” expansion potential. Final expansion potential of site soils should be determined at the completion of grading. Results of expansion testing at finish grades will be utilized to confirm final foundation design.
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3.0 CONCLUSIONS
Based on the results of our geotechnical evaluation, it is our opinion that the proposed development is feasible from a geotechnical standpoint, provided the following conclusions and recommendations are implemented.
The following is a summary of the primary geotechnic al factors that may affect future development of the site:
x In general, field explorations (borings) indicate primarily native soils consisting of variable amounts of sandy clay, sandy silt, sand, silty sand and clayey sand, which are gray to brown, dry to moist, and generally loose/medium stiff to very dense, to the maximum explored depth of approximately 50.5 feet below existing grade. The near-surface loose and compressible soils are not suitable for the planned improvements in their present condition (refer to Section 4.1). x Groundwater was not encountered during our subs urface evaluation to the maximum explored depth of approximately 50.5 feet below current grad e. Historic high groundwater is greater than 100 feet below current grade (CDMG, 1998).
x T h e s u b j e c t s i t e i s n o t l o c a t e d w i t h i n a s t a t e o f C a l i f o r n i a E a r t h q u a k e F a u l t Z o n e ( C G S , 2 0 2 5 ) . T h e main seismic hazard that may affect the site is ground shaking from one of the active regional faults.
The subject site will likely experience strong seismic ground shaking during its design life. x Based on our review of the State of California Department of Conservation, Earthquake Zones of Required Investigation (CGS, 2025), the subject site is not within a liquefaction hazard zone. The potential for liquefaction is considered very low due to the lack of groundwater in the upper 50 feet and very dense on-site soils. However, isolated sand layers may be susceptible to dry sand seismic settlement. Total seismic settlement is estimated to be on the order 0.5-inch. Differential seismic settlement may be estimated as one-half of the total seismic settlement over a horizontal span of 40 feet.
x Based on the results of preliminary laboratory testing, site soils are anticipated to have “Very Low” expansion potential. Final design expansion potent ial must be determined at the completion of grading.
x Some of the onsite soils may not be suitable for retaining wall backfill due to the fines content; therefore, select grading and stockpiling of the onsite sandy soils or import of sandy soils meeting the project requirements should be anticipated by the contractor. x Excavations into the existing site soils should be feasible with heavy construction equipment in good working order. From a geotechnical perspective, the existing onsite soils are suitable material for use as fill, provided that they ar e relatively free from oversized material (larger than 8 inches in maximum dimension), construction debris, and significant organic material. x Oversized material (material larger than 8 inch es in maximum dimension) may be encountered during site grading based on our subsurface evaluation.
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4.0 PRELIMINARY RECOMMENDATIONS
The following recommendations are to be consider ed preliminary and should be confirmed upon completion of grading and earthwork operations. In addition, they should be considered minimal from a geotechnical viewpoint, as there may be more rest rictive requirements from the architect, structural engineer, building codes, governing agencies, or the owner.
It should be noted that the following geotechnical recommendations are intended to provide sufficient information to develop the site in general accordance with the 2022 CBC requirements. With regard to the potential occurrence of potent ially catastrophic geotechnical hazards such as fault rupture, earthquake-induced landslides, liqu efaction, etc. the following geot echnical recommendations should provide adequate protection for the proposed develo pment to the extent required to reduce seismic risk to an “acceptable level.” The “acceptable level” of risk is de fined by the California Code of Regulations as “that level that provides reasonable protection of the public safety, though it does not necessarily ensure continued structural integrity and functionality of the project” [Section 3721(a)].
Therefore, repair and remedial work of the pr oposed improvements may be required after a significant seismic event. With regards to the potential for less significant geologic hazards to the proposed development, the recommendations cont ained herein are intended as a reasonable protection against the potential damaging effects of geotechnical phenomena such as expansive soils, fill settlement, groundwater seepage, etc. It should be understood, however, that although our recommendations are intended to maintain the stru ctural integrity of the proposed development and structures given the site geotechnical conditions, they cannot preclude the potential for some cosmetic distress or nuisance issues to develop as a result of the site geotechnical conditions.
The geotechnical recommendations contained herein must be confirmed to be suitable or modified based on the actual as-graded conditions.
4.1 Site Earthwork
We anticipate that earthwork at the site will consist of the removal of existing improvements associated with the former land use followed by the required earthw ork removals, precise grading, and construction of the proposed new improvemen ts, including the residential structures, subsurface utilities, interior drive alleys, etc.
W e r e c o m m e n d t h a t e a r t h w o r k o n s i t e b e p e r f o r m e d i n a c c o r d a n c e w i t h t h e f o l l o w i n g recommendations, future grading plan review report(s), the 2022 CBC/City of Arcadia grading requirements, and the General Earthwork and Grading Specifications included in Appendix E. In case of conflict, the following recommendations shall supersede those incl uded in Appendix E.
The following recommendations should be consid ered preliminary and may be revised within the future grading plan review report or based on the actual conditions encountered during site grading.
4.1.1 Site Preparation
Prior to grading of areas to receive structural fill or engineered improvements, the areas should be cleared of existing asphalt, surface obstructions, and demolition debris.
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Vegetation and debris should be removed and properly disposed of off-site. Holes resulting from the removal of buried obstructions, which extend below proposed finish grades, should be replaced with suitable compacted fill material. Any abandoned sewer or storm drain lines should be completely removed and replaced with properly placed compacted fill. Deeper demolition may be required in order to remove existing foundations. We recommend the trenches as sociated with demolition which extend below the remedial grading depth be backfilled and properly compacted prior to the demolition contractor leaving the site.
If cesspools or septic systems are encountered, they should be removed in their entirety.
The resulting excavation should be backfilled with properly compacted fill soils. As an alternative, cesspools can be backfilled with lean sand-cement slurry. Any encountered wells should be properly abandoned in accordance with regulatory requirements. At the conclusion of the clearing operations, a representative of LGC Geotechnical should observe and accept the site prior to further grading.
4.1.2 Removal and Recompaction Depths and Limits
In order to provide a relatively uniform bearing condition for the planned building structures, upper loose/compressible soils are to be temporarily removed and recompacted as properly compacted fills. Existing undocumented artificial fill within the i n f l u e n c e o f t h e p r o p o s e d s t r u c t u r a l i m p r o v e m e n t s s h o u l d b e r e m o v e d t o s u i t a b l e , competent native materials prior to placement of artificial fill to design grades. For preliminary planning purposes, the depth of required removals and recompaction may be estimated as indicated below. It should be noted that updated recommendations may be required based on changes to building layouts and/or grading plan.
Buildings: Soils shall be temporarily removed and recompacted to a depth ranging from 5 to 6 feet below existing grade or 3 feet be low the bottom of foundations, whichever is deeper. Refer to the Boring Location Map (Figure 2) for recommended remedial grading depths. Where space is available, the enve lope for removal and recompaction should extend laterally a minimum distance equal to the depth of removal and recompaction below finish grade or 5 feet beyond the ed ges of the proposed building improvements, whichever is larger.
Minor Site Structures: For minor site structur es such as free-standing walls, retaining walls, etc., temporary removal and recompacti on should extend a minimum of 3 feet below existing grade or 2 feet below propos ed footings, whichever is greater. Where space is available, the envelope for removal and recompaction should extend laterally a minimum distance of 3 feet beyond the ed ges of the proposed minor site structure improvements.
Pavement and Hardscape Areas: Within pa vement and hardscape areas, temporary removal and recompaction should extend to a depth of at least 2 feet below existing grade or 2 feet below the bottom of the pavement section, whichever is deeper. Pavement areas encountering undocumented fill materials may require deeper removal and recompaction and should be determined based on the conditions exposed during grading. In general, the envelope for removal and recompaction should extend laterally a minimum lateral
Project No. 25041-01 Page 14 June 26, 2025
distance of 2 feet beyond the edges of the proposed pave ment or hardscape improvements.
Local conditions may be encountered during excavation that could require additional over-excavation beyond the above noted mini mum in order to obtain an acceptable subgrade. The actual depths and lateral extents of grading will be determined by the geotechnical consultant, based on subsurface conditions encountered during grading.
Removal areas and areas to be over-excavated should be accurately staked in the field by the Project Surveyor.
4.1.3 Temporary Excavations
Temporary excavations should be performe d in accordance with project plans, specifications, and all Occupational Safe ty and Health Administration (OSHA) r e q u i r e m e n t s . E x c a v a t i o n s s h o u l d b e l a i d b a c k o r s h o r e d i n a c c o r d a n c e w i t h O S H A requirements before personnel or equipment are allowed to enter.
Based on our field evaluation, site soils within the upper 5 to 10 feet are anticipated to be OSHA Type “B” soils (refer to the attached boring logs). Sandy soils are present and should be considered susceptible to caving. Soil conditions should be regularly evaluated during construction to verify conditions are as anticipated. The contractor shall be responsible for providing the “competent pe rson,” required by OSHA standards, to evaluate soil conditions. Clos e coordination with the geotec hnical consultant should be maintained to facilitate construction while providing safe excavations. Excavation safety is the sole responsibility of the contractor.
Where proposed improvements will be adjace nt to property lines, the potential for impacting existing offsite improvements may be reduced by performing “ABC” slot cuts while performing earthwork removal and recompaction. “ABC” slot cuts are defined as excavations perpendicular to sensitive property boundaries that are divided into multiple “slots” of equal width. If slots are labeled A, B, C, A, B, C, etc., then all “A” slots can be excavated at the same time but must be backfilled before all “B” slots can be excavated, etc. Any given slot should be backfilled immediately with properly compacted fill to finish grade prior to excavation of the adjacent two slots. Please note sands susceptible to caving are present at the si te. Recommendations for slot cut dimensions should be evaluated during grading. Protec tion of the existing offsite improvements during grading is the responsibility of the contractor.
Vehicular traffic, stockpiles, and equipment storage should be set back from the perimeter of excavations a distance equivalent to a 1:1 projection from the bottom of the excavation.
O n c e a n e x c a v a t i o n h a s b e e n i n i t i a t e d , i t s h o u l d b e b a c k f i l l e d a s s o o n a s p r a c t i c a l .
Prolonged exposure of temporary excavations may result in some localized instability.
Excavations should be planned so that they are not initiated without sufficient time to shore/fill them prior to weekends, holidays, or forecasted rain.
It should be noted that any excavation that extends below a 1:1 (horizontal to vertical) p r o j e c t i o n o f a n e x i s t i n g f o u n d a t i o n w i l l r e m o v e e x i s t i n g s u p p o r t o f t h e s t r u c t u r e foundation. If requested, temporary shoring parameter will be provided.
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4.1.4 Removal Bottoms and Subgrade Preparation
In general, removal bottom areas and any ar eas to receive compacted fill should be scarified to a minimum depth of 6 inches, brought to near-optimum moisture content (generally within optimum and 2 percent above optimum moisture content), and re- compacted per project recommendations.
Removal bottoms, over-excavation bottoms and areas to receive fill should be observed and accepted by the geotechnical consultant prior to subsequent fill placement. Soil subgrade for planned footings and improvements (e.g., slabs, etc.) should be firm and competent.
4.1.5 Material for Fill
From a geotechnical perspective, the onsite soils are generally considered suitable for use as general compacted fill, provided they are screened of or ganic materials, construction debris, and oversized material (8 inches in greatest dimension).
From a geotechnical viewpoint, any required import soils for general fill (i.e., non- retaining wall backfill) should consist of clea n, granular soils of “Very Low” expansion potential (expansion index 20 or less based on ASTM D 4829), and generally free of organic materials, construction debris and material greater than 3 inches in maximum dimension. Import for required retaining wall backfill should meet the criteria outlined in t h e f o l l o w i n g p a r a g r a p h . S o u r c e s a m p l e s s h o u l d b e p r o v i d e d t o t h e g e o t e c h n i c a l consultant for laboratory testing a minimu m of four working days prior to planned importation.
Retaining wall backfill should consist of sandy soils with a maximum of 35 percent fines (passing the No. 200 sieve) per American Society for Testing and Materials (ASTM) Test Method D1140 (or ASTM D6913/D422) and a “Very Low” expansion potential (EI of 20 or less per ASTM D4829). Soils should also be screened of organic materials, construction debris, and any material greater than 3 inches in maximum dimension. Some of the onsite soils may not be suitable for retaining wall backfill due to fines content; therefore, select grading and stockpiling of the onsite sandy soils or import of sandy soils meeting the criteria outlined above should be anticipate d by the contractor for obtaining suitable retaining wall backfill soil.
Aggregate base (crushed aggregate base or crushed miscellaneous base) should conform to the requirements of Section 200-2 of the Standard Specifications for Public Works Construction (“Greenbook”) for untrea ted base materials (except processed miscellaneous base) or Caltrans Class 2 aggregate base.
The placement of demolition materials in compacted fill is acceptable from a geotechnical viewpoint provided the demolition material is broken up into pieces not larger than approximately 2 to 4 inches in maximum dimension, and well blended into fill soils with essentially no resulting voids. Demolition m a t e r i a l p l a c e d i n f i l l s m u s t b e f r e e o f construction debris (wood, brick, etc.) and reinforcing steel. If asphalt concrete fragments will be incorporated into the demolition ma terials, approval from an environmental
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viewpoint may be required and is not the pu rview of the geotechnical consultant. From our previous experience, we recommend that asphalt concrete fragments be limited to fill areas within planned streets, alleys or non-structural areas (i.e., not within building pad areas).
4.1.6 Placement and Compaction of Fills
Material to be placed as fill should be brought to near-optimum moisture content (generally within optimum and 2 percent above optimum moisture content) and recompacted to at least 90 percent relative compaction (per ASTM D1557). Moisture conditioning of site soils will be required in order to achieve adequate compaction. Soils will generally require additional moisture in order to achieve the required compaction.
Drying and/or mixing the very moist soils may also be required prior to reusing the materials in compacted fills.
The optimum lift thickness to produce a uniformly compacted fill will depend on the type and size of compaction equipment used. In general, fill should be placed in uniform lifts not exceeding 8 inches in compacted thickness. Each lift should be thoroughly compacted and accepted prior to subsequent lifts. Generally, placement and compaction of fill should be performed in accordance with local gr ading ordinances and with observation and testing performed by the geotechnical consultant. Oversized material as previously defined should be removed from site fills. During backfill of excavations, the fill should be properly benched into firm and competent soils of temporary backcut slopes as it is placed in lifts.
Aggregate base material should be compacted to at least 95 percent relative compaction a t o r s l i g h t l y a b o v e o p t i m u m m o i s t u r e c o n t e n t p e r A S T M D 1 5 5 7 . S u b g r a d e b e l o w aggregate base should be compacted to at least 90 percent relative compaction per ASTM D1557 at or slightly above optimum moisture content (generally within optimum and 2 percent above optimum moisture content).
I f g a p - g r a d e d ¾ - i n c h r o c k i s u s e d f o r b ackfill (around storm dr ain storage chambers, retaining wall backfill, etc.) it will require co mpaction. Rock shall be placed in thin lifts (typically not exceeding 6 inches) and mech anically compacted with observation by geotechnical consultant. Backfill rock shall meet the requirements of ASTM D2321. Gap- graded rock is required to be entirely wrapped in filter fabric (Mirafi 140N or approved alternative) or at the very minimum to be vertically separated from the trench backfill with filter fabric to prevent the migration of fines into the rock backfill.
4.1.7 Trench and Retaining Wall Backfill and Compaction
The onsite soils will generally be suitable as trench backfill, provided the soils are screened of rocks and other material greate r than 6 inches in diameter, construction debris and organic matter. Trench backfill should be compacted in uniform lifts (generally not exceeding 12 inches in co mpacted thickness) by mechan ical means to at least 90 percent relative compaction (per ASTM Test Method D1557). If trenches are shallow or the use of conventional equipment may result in damage to the utilities, sand having a
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s a n d e q u i v a l e n t ( S E ) o f 3 0 o r g r e a t e r ( p e r C a l i f o r n i a T e s t M e t h o d [ C T M ] 2 1 7 ) m a y b e used to bed and shade the pipes. Sand backfill within the pipe bedding zone may be densified by jetting or flooding and then tamped to ensure adequate compaction. Sand g r a i n s s h o u l d b e f r o m a n a t u r a l s o u r c e w i t h r o u n d e d s h a p e . M a n u f a c t u r e d s a n d f r o m crushed rock or recycled material is not suit able for jetting/flooding as the grains are typically angular in shape and do not densify well enough with these methods.
Manufactured sand can be used as shading material when mechanical compaction efforts are used. Subsequent trench backfill should be compacted in uniform thin lifts by mechanical means to at least a minimum 90 percent relative compaction (per ASTM D1557). If any ¾-inch rock is used for backfill, see Section 4.1.6 for filter fabric requirements.
Retaining wall backfill should consist of onsite or imported select sandy soils as outlined in preceding Section 4.1.5. The limits of select sandy backfill should extend a minimum ½ the height of the retaining wall or the width of the heel (if applicable), whichever is greater, refer to Figure 3. Retaining wall back fill soils should be compacted in relatively uniform thin lifts to at least 90 percent relative compaction (per ASTM D1557). Jetting or flooding of retaining wall backfill materials should not be permitted.
In backfill areas where mechanical compaction of soil backfill is impractical due to space constraints, typically sand-cement slurry may be substituted for compacted backfill. The slurry should contain about one sack of cement per cubic yard. When set, such a mix typically has the consistency of compacted soil. Sand cement slurry placed near the surface within landscape areas should be evaluated for potential impacts on planned improvements.
A representative from LGC Geotechnical should observe, probe, and test the backfill to verify compliance with the project recommendations.
4.1.8 Shrinkage and Subsidence
Allowance in the earthwork volumes budget should be made for an estimated 5 to 20 percent reduction (shrink) in volume of near-surface (upper approximate 5 feet) soils. It should be stressed that these values are on ly estimates and that an actual shrinkage factor would be extremely difficult to pr edetermine. Subsidence, due to earthwork operations, is expected to be on the order of 0.1 feet. These values are estimates only and exclude losses due to removal of vegetation or debris. The effective shrinkage of onsite soils will depend primarily on the type of compaction equipment and method of compaction used onsite by the contractor and accuracy of the topographic survey.
Due to the combined variability in topographi c surveys, inability to precisely model the removals and variability of on-site near-surface conditions, it is our opinion that the site will not balance at the end of grading. If importing/exporting a large volume of soils is not considered feasible or econom ical, we recommend a balance area be designated onsite t h a t c a n f l u c t u a t e u p o r d o w n b a s e d o n t h e a c t u a l v o l u m e o f s o i l . W e r e c o m m e n d a “balance” area that can accommodate on the order of 5 percent (plus or minus) of the total grading volume be considered.
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4.2 Preliminary Foundation Recommendations
Provided that the remedial grading recommendations provided herein are implemented, the site may be considered suitable for the support of the residential structures using a conventional or post-tensioned foundation system designed to resist the impacts of expansive soils. Site soils are anticipated to be “Very Low” expansion potential (EI of 20 or less per ASTM D4829) and special design considerations from a geotechnical perspective are not required. The structural designer should use their own judgment in the design of the foundation system. Please note that the following foundation recommendations are preliminary and must be confirmed by LGC Geotechnical at the completion of grading.
Preliminary foundation recommendations are provided in the following sections. Recommended soil bearing and estimated settlement due to structural loads are provided in Section 4.3. The foundation should be designed in consideration of the site seismic settlement as outlined in Section 2.5.1.
4.2.1 Provisional Conventional Foundation Design Parameters
Due to the very low expansion potential of the onsite soils, the foundation/structural engineer may design a conventional foundation system that is tied together based upon the anticipated dead and live loads (wind, seismic) that will be imparted by the structure. The recommendations provided in the “Soil Bearing and Lateral Resistance” section may be utilized in the design of a rigid slab-on-grade conventional foundation designed in accordance with Section 1808 of the 2022 C.B.C.
4.2.2 Provisional Post-Tensioned Foundation Design Parameters
The foundation designer may use a modulus of vertical subgrade reaction (k) of 200 pounds per cubic inch (pounds per square inch per inch of deflection). This value is for a 1-foot by 1-foot square loaded area and sh ould be adjusted by the structural designer for the area of the proposed footing using the following formula:
k = 200 x [(B+1)/2B]2
k = modulus of vertical subgrade reaction, pounds per cubic inch (pci) B = foundation width (feet)
The moisture content of near surface fill soils should be kept at optimum moisture content to a minimum depth of 12 inches prior to trenching and concrete placement.
4.2.3 Foundation Subgrade Preparation and Maintenance
The geotechnical parameters provided herein assume that if the areas adjacent to the foundation are planted and irrigated, these areas will be designed with proper drainage and adequately maintained so that ponding, which causes significant moisture changes below the foundation, does not occur. Our recommendations do not account for excessive irrigation and/or incorrect landscape design. Plants should only be provided
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with sufficient irrigation for life and not overwatered to saturate subgrade soils. Sunken planters placed adjacent to the foundation sh ould either be designed with an efficient drainage system or liners to prevent moisture infiltration below the foundation. Some lifting of the perimeter foundation beam should be expected even with properly constructed planters.
In addition to the factors mentioned above, future owners/property management p e r s o n n e l s h o u l d b e m a d e a w a r e o f t h e p o t e n t i a l n e g a t i v e i n f l u e n c e s o f t r e e s a n d / o r other large vegetation. Roots that extend near the vicinity of foundations can cause distress to foundations. Future owners (and the owner’s landscape architect) should not plant trees/large shrubs closer to the foundations than a distance equal to half the mature height of the tree or 20 feet, whichever is more conservative unless specifically provided with root barriers to prevent root growth below the building foundation.
It is the owner’s responsibility to perfor m periodic maintenance during hot and dry periods to ensure that adequate watering has been provided to keep soil from separating or pulling back from the fo undation. Future owners and property management personnel should be informed and educated regarding the importance of maintaining a constant level of soil-moisture. The owners should be made aware of the potential negative consequences of both excessive watering, as well as allowing potentially expansive soils to become too dry. Expansive soils can undergo shrinkage during drying, and swelling during the rainy winter season, or when irrigation is resumed. This can result in distress to building structures and hardscape improvements. The builder should provide these recommendations to future owners and property management personnel.
4.2.4 Slab Underl ayment Guidelines
The following recommendations are for informational purposes since they are unrelated to the geotechnical performance of the foundation. Some post-construction moisture migration should be expected belo w the foundation; the foundation engineer must assume soil moisture to be present below the slab. The following recommendations may be superseded by the foundation engineer and/or owner.
In general, interior floor slabs with moisture sensitive floor coverings should be underlain by a minimum 10-15 mil thick vapor retarder, which has a water vapor transmission rate (permeance) of less than 0.3 perms, as determined by ASTM E 96, and meets the applicable code requirements (ASTM E 1745).
It is the responsibility of the contractor to ensure that the moisture/vapor retarder systems are properly installed in accordance with the project plans and manufacturer’s specifications, and that the moisture/vapor retarder materials are free of tears and punctures prior to and as a result of concre te placement. Additional moisture reduction and/or prevention measures may be needed, depending on the performance requirements of future interior floor coverings.
The foundation engineer/architect should determine whether the use of a capillary break (sand or gravel layer) in conjunction with the vapor retarder is necessary or
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required by code. Sand layer thickness and location (above and/or below vapor retarder) should also be determined by the foundation engineer/architect.
4.3 Soil Bearing and Lateral Resistance
Provided our earthwork recommendations are implemented, an allowable soil bearing pressure of 2,000 pounds per square foot (psf) may be used for the design of footings having a minimum width of 12 inches and minimum embedment of 12 inches below lowest adjacent ground surface.
This value may be increased by 300 psf for each additional foot of em bedment and 150 psf for each additional foot of foundation width to a maximum value of 3,000 psf. A post-tensioned mat foundation a minimum of 6 inches below lowest adjacent grade may be designed for an allowable soil bearing pressure of 1,200 psf. These allo wable bearing pressures are applicable for level (ground slope equal to or flatter than 5H:1V) co nditions only. Bearing values indicated are for
loading (i.e., wind or seismic loads).
In utilizing the above-mentioned allowable be aring capacity and pr ovided our earthwork recommendations are implemented, foundation settlement due to structural loads is anticipated to be 1-inch or less. Differential static settlement may be taken as half of the static settlement (i.e., ½-inch over a horizontal span of 40 feet). Recommendations for estimated seismic settlement are provided in Section 2.5.1.
Res is tanc e to late ral loa d s c an be p rov id ed by fric tion ac ting a t the bas e of found ations and by passive earth pressure. For concrete/soil frictional resistance, an allowable coefficient of friction of 0.35 may be assumed with dead-load forces. For slabs constructed over a moisture retarder, the allowable friction coefficient should be prov ided by the manufacturer. An allowable passive lateral earth pressure of 250 psf per foot of depth (or pcf) to a maximum of 2,500 psf may be used for the sides of footings poured against properly compacted fill. Allowable passive pressure may be increased to 340 pcf (maximum of 3,400 psf) for short duration seismic loading. This passive pressure is applicable for level (ground slope equal to or flatter than 5H:1V) conditions.
For a 2:1 (horizontal to vertical) downward sloping condition, a reduced passive lateral earth pressure of 100 pcf to a maximum of 1,000 psf may be used. This allowable passive pressure may be increased to 135 pcf to a maximum of 1,350 psf for short duration seismic loading.
Frictional resistance and passive pressure may be used in combination without reduction. We recommend that the upper foot of passive resistan ce be neglected if finished grade will not be covered with concrete or asphalt. The provided allowable passive pressures are based on a factor of safety of 1.5 and 1.1 for static and seismic loading conditions, respectively.
4.4 Lateral Earth Pressures for Retaining Walls
Lateral earth pressures for approved native sa ndy or import soils meeting indicated project requirements are provided below. Lateral earth pressures are provided as equivalent fluid unit weights, in psf per foot of depth (or pcf). These values do not contain an appreciable factor of safety, so the retaining wall designer should appl y the applicable factors of safety and/or load factors during design. A soil unit weight of 120 pcf may be assumed for calculating the actual weight of soil over the wall footing.
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The following lateral earth pressures are presented in Table 3 below for approved granular soils with a maximum of 35 percent fines (passing the No. 200 sieve per ASTM D-421/422) and a “Very Low” expansion potential (EI of 20 or less per ASTM D4829). Some of the onsite soils may not be suitable for retaining wall backfill due to fines content; therefore, select grading and stockpiling of the onsite soils or import of soil s meeting the criteria outlined above should be anticipated by the contractor for obtaining suitable retaining wall backfill soil. The wall designer should clearly indicate on the retaining wall plans the required select sandy soil backfill criteria.
These preliminary findings should be confirmed during grading.
TABLE 3
Lateral Earth Pressures – Approved Onsite or Imported Sandy Soils
Conditions
Equivalent Fluid Unit
Weight (pcf)
Equivalent Fluid Unit
Weight (pcf)
Level Backfill 2:1 Sloped Backfill
Approved Sandy Soils Approved Sandy Soils
Active 35 55
At-Rest 55 70
If the wall can yield enough to mobilize the full sh ear strength of the soil, it can be designed for “active” pressure. If the wall cannot yield unde r the applied load, the earth pressure will be higher. This would include 90-degree corners of re taining walls. Such walls should be designed for “at-rest.” The equivalent fluid pressure values assume free-draining conditions. If conditions other than those assumed above are anticipated, the equivalent fluid pressure values should be provided on an individual-case basis by the geotechnical engineer.
R e t a i n i n g w a l l s t r u c t u r e s s h o u l d b e p r o v i d e d w i t h a p p r o p r i a t e d r a i n a g e a n d a p p r o p r i a t e l y waterproofed. To reduce, but not eliminate, saturation of near-surface (upper approximate 1- foot) soils in front of the retaining walls, the pe rforated subdrain pipe should be located as low as possible behind the retaining wall. The outlet pipe should be sloped to drain to a suitable o u t l e t . I n g e n e r a l , w e d o n o t r e c o m m e n d r e t a i n i n g w a l l o u t l e t p i p e s b e c o n n e c t e d t o a r e a drains. If subdrains are connected to area drains, special care and information should be provided to homeowners to maintain these drains. Typical retaining wall drainage is illustrated in Figure 3. It should be noted that the recommended subdrain does not provide protection against seepage through the face of the wall and/ or efflorescence. Efflor escence is generally a white crystalline powder (discoloration) that results when water containing soluble salts m i g r a t e s o v e r a p e r i o d o f t i m e t h r o u g h t h e f a c e o f a r e t a i n i n g w a l l a n d e v a p o r a t e s . I f s u c h seepage or efflorescence is undesirable, retainin g walls should be waterp roofed to reduce this potential. Please note that waterproofing an d outlet systems are not the purview of the geotechnical consultant.
Surcharge loading effects from any adjacent stru ctures should be evaluated by the retaining wall designer. In general, structural loads within a 1:1 (horizontal to vertical) upward
Project No. 25041-01 Page 22 June 26, 2025
projection from the bottom of the proposed retaining wall foot ing will surcharge the proposed retaining wall. In addition to the recommended earth pressure, retaining walls adjacent to streets should be designed to resist a unifor m lateral pressure of 80 pounds per square foot (psf) due to normal street vehicle traffic if applicable. Uniform lateral surcharges may be estimated using the applicable coefficient of lateral earth pressure using a rectangular distribution. A factor of 0.45 and 0.3 may be used for at-rest and active conditions, respectively.
The retaining wall designer should contact th e geotechnical engineer for any required geotechnical input in estimating any applicable surcharge loads.
If retaining walls greater than 6 feet in height are proposed, the retaining wall designer should contact the geotechnical engineer for specific seismic lateral earth pressure increments based on the configuration of the planned retaining wall structures.
Soil bearing and lateral resistan ce (friction coefficient and passive resistance) are provided in Section 4.3. Earthwork considerations (temporary backcuts, backfill, compaction, etc.) for retaining walls are provided in Section 4.1 (S ite Earthwork) and the subsequent earthwork related sub-sections.
4.5 Control of Surface Water and Drainage Control
From a geotechnical perspective, positive draina ge of surface water away from structures is v e r y i m p o r t a n t . W a t e r s h o u l d n o t b e a l l o w e d t o p o n d a d j a c e n t t o b u i l d i n g s o r t o f l o w f r e e l y down a graded slope. Per section 1804.4 of the 2022 CBC, positive drainage may be accomplished by providing drainage away from bu ildings at a gradient of at least 5 percent for earthen surfaces for a distance of at least 10 feet away from the face of wall. If a distance of 10 feet cannot be achieved, an alternative of a gradie nt of at least 5 percent to an area drain or swale having a gradient of 2 percent is accept able. Where necessary, drainage paths may be shortened by use of area drains and collector pipes. Eave gutters are recommended and should reduce water infiltration into the subgrade soils if the downspouts are properly connected to appropriate outlets. Ultimately surface drainage and code compliance are the purview of the project civil engineer.
Planters with open bottoms adjacent to building s should be avoided. Planters should not be designed adjacent to buildings unless provisions for drainage, such as catch basins, liners, and/or area drains, are made. Overwatering must be avoided.
P l a n t e r s a d j a c e n t t o a b u i l d i n g o r s t r u c t u r e s h o u l d b e a v o i d e d w h e r e v e r p o s s i b l e o r b e properly designed (e.g., lined with a membrane), to reduce the penetration of water into the adjacent footing subgrades and thereby reduce moisture related damage to the foundation.
P l a n t i n g a r e a s a t g r a d e s h o u l d b e p r o v i d e d with appropriate positive drainage. Wherever possible, exposed soil areas should be above ad jacent paved grades to facilitate drainage.
Planters should not be depressed below adjacent paved grades unless provisions for drainage, such as multiple depressed area drains, are cons tructed. Adequate drainage gradients, devices, a n d c u r b i n g s h o u l d b e p r o v i d e d t o p r e v e n t r u n o f f f r o m a d j a c e n t p a v e m e n t o r w a l k s i n t o t h e p l a n t i n g a r e a s . I r r i g a t i o n m e t h o d s s h o u l d p r o m o t e u n i f o r m i t y o f m o i s t u r e i n p l a n t e r s a n d beneath adjacent concrete flatwork. Overwateri ng and underwatering of landscape areas must be avoided.
Project No. 25041-01 Page 23 June 26, 2025
Area drain inlets should be maintained and kept clear of debris in order to properly function.
H o m e o w n e r s s h o u l d a l s o b e m a d e a w a r e t h a t e x c e s s i v e i r r i g a t i o n o f n e i g h b o r i n g p r o p e r t i e s can cause seepage and moisture conditions on ad jacent lots. Homeowners should be furnished with these recommendations communicating the importance of maintaining positive drainage away from structures, towards streets, when they design their improvements.
T h e i m p a c t o f h e a v y i r r i g a t i o n o r i n a d e q u a t e runoff gradients can create perched water conditions. This may result in seepage or shallow groundwater conditions where previously none existed. Maintaining adequate surface drainage and controlled irrigation will significantly reduce the potential for nuisance-type moisture problems. To reduce differential earth movements such as heaving and shrinkage due to the change in moisture content of foundation soils, which may cause distress to a residential structure and associated improvements, moisture content of the soils surrounding the structure should be kept as relatively constant as possible.
Subdrains and v-ditches must be properly maintained, and their outlets kept free draining and clear of any potential obstructions. Routine maintenance should be performed, especially prior to and during the rainy season. Failure to properly maintain these elements may result in slope failures, slumps, excessive erosion, localized saturated zones, nuisance type water issues, etc.
Any future trenches excavated on a slope face for utility or irrigation lines and/or for any purpose should be properly backfilled and compacted to the slope face. Observation/testing and acceptance by the geotechnical consultant during trench backfill are recommended.
A program for the elimination of burrowing animals in both native and graded slope areas must be established and properly maintained to protec t slope stability by reducing the potential for surface water to penetrate into the soil. Cont inuous erosion control, rodent control, and maintenance are essential to the long-term stability of all slopes.
4.6 Subsurface Water Infiltration
It should be noted that intentionally infiltrati ng storm water conflicts with the geotechnical engineering objective of directing surface wate r away from structures and improvements. The geotechnical stability and integrity of a site is reliant upon appropriately handling surface water.
In general, the vast majority of geotechnical distress issues are directly related to improper drainage. Distress in the form of movement of foundations and other improvements could occur as a result of soil saturation and loss of soil support of foundations and pavements, settlement, collapse, internal soil erosion, and/or expansion. Additionally, off-site properties and improvements may be subjected to seepage, spri ngs, instability, movements of foundations or other impacts as a result of water infiltrati on and migration. Infi ltrated water may enter underground utility pipe zones or other highly permeable layers and migrate laterally along these layers, potentially impacting other improv ements located far away from the point of infiltration. Any proposed infiltration system should not be located near slopes or settlement sensitive existing/proposed improvements in order to reduce the potential for slope failures and geotechnical distress issues related to infiltration.
If water must be infiltrated due to regulato ry requirements, we recommend the absolute
Project No. 25041-01 Page 24 June 26, 2025
minimum amount of water be infiltrated and that the infiltration areas not be located near settlement-sensitive existing/proposed improvements, basement/retaining walls, or any slopes.
As with all systems that are designed to concen trate surface flow and direct the water into the subsurface soils, some minor settlement, nuisance type localized saturation and/or other water related issues should be expected. Due to variability in geologic and hydraulic conductivity characteristics, these effects ma y be experienced at the onsite location and/or potentially at other locations beyond the physical limits of the subject site. Infiltrated water may enter underground utility pipe zones or flow along heterogeneous soil layers or geologic structure and migrate laterally impacting other improvements which may be located far away or at an elevation much lower than the infiltration source. Recommendations for subsurface water infiltration are provided below.
The design infiltration rate is determined by dividing the infiltration rate by total reduction factor. The total reduction factor is calculated from a series of reduction factors, including; test procedure (RFt), site variability (RF v) and long-term siltation plugging and maintenance (RF s) as presented listed in Table 4 below (RF t + RFv + RFs). Based on the Los Angeles County testing guidelines (2021), the reduction factor for long-term siltation plugging and maintenance (RF s) is the purview of the infiltration system designer.
TABLE 4
Shallow Surface Infiltration - Reduction Factors Applied to Infiltration Rate
Consideration Reduction Factor
Test procedure, boring percolation, RFt 1.0
Site variability, number of tests, etc., RFv 1.5
Long-term siltation plugging and maintenance, RFs TBD* Total Reduction Factor, RF = RFt + RFv + RFs TBD*
*Reduction Factor for long-term siltation plugging and maintenance to be confirmed by civil engineer
Per the requirements of the Los Angeles County testing guidelines (2021), subsurface materials shall have a design infiltration rate equal to or greater than 0.3 inches per hour. The Total Reduction Factor for test procedure, site variability considerations, and long-term siltation plugging and maintenance (RFt, RFv, and RFs) and the design infiltration rate will be determined by the civil engineer. Results of infiltration testing are provided in Appendix D.
The following should be considered for the design of any expected infiltration system.
x We recommend a minimum setback of 15 feet fr om the limits of the proposed infiltration system to structural improvements.
x W e r e c o m m e n d t h e d e s i g n o f a n y i n f i l t r a t i o n system include at leas t one redundancy or overflow system. It may be prudent to provide an overflow system directly connected to the storm drain system in order to prevent failure of the infiltration system, either as a result of lower than anticipated infiltration and/or very high flow volumes.
Project No. 25041-01 Page 25 June 26, 2025
x Water discharge from any infiltration systems should not occur within the zone of influence of foundation footings (column and load bearing wall locations). x An adequate setback distance be tween any infiltration facility and adjace nt property lines should be maintained.
x The infiltration values provided are based on clean water and this requires the removal of trash, debris, soil particles, etc., and on-going maintenance. Over time, siltation and plugging may reduce the infiltration rate and subsequent effectiveness of the infiltration system. It should be noted that methods to prevent this shall be the responsibility of the infiltration designer and are not the purview of the geotechnical co nsultant. If adequate measures cannot be incorporated into the de sign and maintenance of the system, then the infiltration rates may need to be further reduced. These and other factors should be considered in selecting a design infiltration rate.
x Any designed infiltration system will require routine periodic maintenance. x Contamination and environmental suitability of the site for infiltration was not evaluated by us and should be evaluated by others (environmental consultant). We only addressed the geotechnical issues associated with stormwater infiltration.
LGC Geotechnical should be provided with details for any planned required infiltration system early in the design process for geotechnical input.
4.7 Preliminary Asphal t Pavement Sections
For the purpose of these prelim inary recommendations, we have selected a preliminary design R-value of 40 (assumed) and calculated pavement sections for assumed Traffic Indices (TI) of 5.0 (or less) and 6.0. These recommendations must be confirmed with R-Value testing of representative near-surface soils at the comple tion of grading and afte r underground utilities have been installed and backfilled. Final street sections should be confirmed by the project civil engineer based upon the final design Traffic Index. Determination of the TI is not the purview of the geotechnical consultant. If requested, LGC Geotechnical will provide sections for alternate TI values. Should the city of Arcadia have more stringent requirements, updated pavement recommendations can be provided.
TABLE 5
Preliminary Pavement Sections
Assumed Traffic Index 5.0 (or less) 6.0
R -Value Subgrade 40 40
AC Thickness 4.0 inches 4.0 inches
Base Thickness 5.0 inches 7.0 inches
Due to anticipated construction traffic prior to completion of the project, we recommend that the total thickness (base course and capping course) of AC be placed at essentially the same time. Construction traffic loading on only the base course of the AC will increase the potential for pavement distress. It should be noted that co nstruction traffic such as concrete trucks will
Project No. 25041-01 Page 26 June 26, 2025
likely exceed traffic loading after completion of construction. Additionally, earth moving equipment should not be allowed to drive on pa ved surfaces. The weights of these vehicles far exceed the limits of the pavement and will cause distress, likely requiring the pavement sections to be removed and replaced.
The pavement section thicknesses provided above are considered minimum thicknesses.
Increasing the thickness of any or all of the above layers will reduce the likelihood of the pavement experiencing distress during its serv ice life. The above recommendations are based on the assumption that proper maintenance and irrigation of the areas adjacent to the roadway will occur throughout the design life of th e pavement. Failure to maintain a proper maintenance and/or irrigation program may jeopardize the integrity of the pavement.
Earthwork recommendations regarding aggregat e base and subgrade are provided in the previous Section 4.1 (Site Earthwork) and the related sub-sections of this report.
P l e a s e n o t e t h a t a s t h e g e o t e c h n i c a l c o n s u l t a n t o f r e c o r d w e w i l l o n l y b e p e r f o r m i n g temperature checks of the asphalt and testing the wet density for calculating relative compaction. We recommend obtaining the services of others if material testing and evaluation o f t h e q u a l i t y o f w o r k m a n s h i p b y t h e c o n t r a c t o r i s d e s i r e d o r r e q u i r e d b y t h e r e g u l a t o r y agency.
4.8 Soil Corrosivity
Although not corrosion engineers (LGC Geotechnical is not a corrosion consultant), several governing agencies in Southern California require the geotechnical consultant to determine the corrosion potential of soils to buried concrete and metal facilities. We therefore present the results of our testing with regard to corrosion for the use of the client and other consultants, as they determine necessary.
Results of the corrosion testing indicated a soluble sulfate content ranging from approximately 8 to 32 parts per million (ppm), chloride conten t ranging from 28 to 29 ppm, pH value range of
7.4 to 7.6, and minimum resistivity value ra nging from 13,400 to 15,410 ohm-cm. Note that based on minimum resistivity the soils are considered moderately corrosive to metallic improvements. If improvements that may be su sceptible to corrosion are proposed, it is recommended that further evaluation by a corrosion engineer be performed.
Based on our laboratory test results of representa tive site soil samples, onsite soils should be considered as having a severity categorization of “not applicable” and are designated class “S0” per ACI 318, Table 19.3.1.1 with respect to sulfates. Concrete in direct contact with the onsite soils can be designed according to ACI 318, Table 19.3.2.1 using the “S0” sulfate classification.
L a b o r a t o r y t e s t i n g m a y n e e d t o b e p e r f o r m e d a t t h e c o m p l e t i o n o f g r a d i n g b y t h e p r o j e c t corrosion engineer to further evaluate the as-graded soil corrosivity characteristics, including sulfate, chloride, pH, minimum resistivity, et c. and provide design level recommendations.
Accordingly, revision of the corrosion potential may be needed, should future test results differ substantially from the conditions reported herein. The client and/or other members of the development team should consider this during the design and planning phase of the project and formulate an appropriate course of action.
Project No. 25041-01 Page 27 June 26, 2025
4.9 Nonstructural Concrete Flatwork
Nonstructural concrete flatwork (such as walkwa ys, bicycle trails, patio slabs, etc.) has a potential for cracking due to changes in soil vo lume related to soil-moisture fluctuations. To reduce the potential for excessive cracking and li fting, concrete may be designed in accordance with the minimum guidelines outlined in Tabl e 6 below. These guidelines will reduce the potential for irregular cracking and promote cracking along construction joints but will not eliminate all cracking or lifting. Thickening the concrete and/or adding additional reinforcement will further reduce cosmetic distress.
TABLE 6
Nonstructural Concrete Flatwork Guidelines for Very Low Expansion Potential
Community
Sidewalks
ȋζ4 feet wide)
Patios/ Walkways
(adjacent to homes
ε4 feet
wide)
Private
Vehicular
Driveways
City Sidewalk
Curb and
Gutters
Minimum
Thickness (in.) 4 (full) 4 (full) 4 (full) City/Agency
Standard
Presoaking Wet down prior
to placing
Wet down prior
to placing
Wet down prior
to placing
City/Agency
Standard
Reinforcement
No. 3 at 24
inches on
centers
No. 3 at 24
inches on
centers
City/Agency
Standard
Thickened
Edge (in.) 8 x 8 City/Agency
Standard
Crack Control
Joints
Saw cut or deep
open tool joint to
a minimum of 1/3
the concrete
thickness
Saw cut or deep
open tool joint
to a minimum
of 1/3 the
concrete
thickness
Saw cut or deep
open tool joint
to a minimum
of 1/3 the
concrete
thickness
City/Agency
Standard
Maximum
Joint Spacing 5 feet 6 feet
10 feet or
quarter cut
whichever is
closer
City/Agency
Standard
To reduce the potential for driveways to separate from the garage slab, the builder may elect to install dowels to tie these two elements together. Similarly, future homeowners should consider the use of dowels to connect flatwork to the foundation.
Project No. 25041-01 Page 28 June 26, 2025
4.10 Geotechnical Plan Review
When available, project plans (g rading, foundation, retaining wall, etc.) should be reviewed by LGC Geotechnical in order to verify our ge otechnical recommendations are implemented.
Updated recommendations and/or additional fieldwork may be necessary.
4.11 Geotechnical Observation and Testing During Construction
The recommendations provided in this report are based on limited subsurface observations and geotechnical analysis. Th e interpolated subsurface conditions should be checked in the field during construction by a representative of LGC Geotechnical. Geotechnical observation and testing is required per Section 1705 of the 2022 CBC.
Geotechnical observation and/or testing should be performed by LGC Geotechnical at the following stages:
x During grading (removal bottoms, fill placement, etc.); x During retaining wall backfill and compaction;
x During utility trench backfill and compaction;
x After presoaking building pads and other concrete-flatwork subgrades, and prior to placement of aggregate base or concrete;
x Preparation of pavement subgrade and placement of aggregate base; x After building and wall footing excavation and prior to placing reinforcement and/or concrete; and
x When any unusual soil conditions are enco untered during any construction operation subsequent to issuance of this report.
Project No. 25041-01 Page 29 June 26, 2025
5.0 LIMITATIONS
Our services were performed using the degree of care and skill ordinarily exercised, under similar circumstances, by reputable soils engineers and geologists practicing in this or similar localities. No other warranty, expressed or implied, is made as to the conclusions and professional advice included in this report.
T h i s r e p o r t i s b a s e d o n d a t a o b t a i n e d f r o m l i m i t e d o b s e r v a t i o n s o f t h e s i t e , w h i c h h a v e b e e n extrapolated to characterize the site. While the scop e of services performed is considered suitable to adequately characterize the site geotechnical conditions relative to the proposed development, no practical evaluation can completely eliminate un certainty regarding the an ticipated geotechnical conditions in connection with a subject site. Variations may exist and conditions not observed or described in this report may be encountered during grading and construction.
T h i s r e p o r t i s i s s u e d w i t h t h e u n d e r s t a n d i n g t h a t i t i s t h e r e s p o n s i b i l i t y o f t h e o w n e r , o r o f h i s / h e r representative, to ensure that the information and recommendations contained herein are brought to the attention of the other consultants (at a minimum the civil engineer, structural engineer, landscape architect) and incorporated into their plans. The contractor should properly implement the recommendations during construction and notify the owner if they consider any of the recommendations presented herein to be unsafe, or unsuitable.
The findings of this report are valid as of the presen t date. However, changes in the conditions of a site can and do occur with the passage of time, whether they be due to natural processes or the works of man on this or adjacent properties. The findings, conclusions, and recommendations presented in this report can be relied upon only if LGC Geotechnical has the opportunity to observe the subsurface c o n d i t i o n s d u r i n g g r a d i n g a n d c o n s t r u c t i o n o f t h e p r o j e c t , i n o r d e r t o c o n f i r m t h a t o u r p r e l i m i n a r y findings are representative for the site. This report is intended exclusively for use by the client, any use of or reliance on this report by a third party shall be at such party’s sole risk.
In addition, changes in applicable or appropriat e standards may occur, whether they result from legislation or the broadening of knowledge. Accordingly, the findings of this report may be invalidated wholly or partially by changes outside our control. Therefore, this report is subject to review and modification.
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Appendix A
References
Project No. 25041-01 A-1 June 26, 2025
APPENDIX A
References
A m e r i c a n C o n c r e t e I n s t i t u t e , 2 0 1 9 , B u i l d i n g C o d e R e q u i r e m e n t s f o r S t r u c t u r a l C o n c r e t e ( A C I 3 1 8 - 1 9 ) and Commentary (ACI 318R-19).
American Society of Civil Engineers (ASCE), 2017, Minimum Design Loads for Buildings and Other Structures, ASCE/SEI 7-16, 2017.
________, 2018, Standard 7-16, Minimum Design Loads for Buildings and Associated Criteria for Buildings and Other Structures, Supplement 1, effective: December 12, 2018.
American Society for Testing and Materials (ASTM), Volume 04.08 Soil and Rock (I): D420 – D5876.
Bray, J.D., and Sancio, R. B., 2006, Assessment of Liquefaction Susceptibility of Fine-Grained Soils, Journal of Geotechnical and Geoenvironmental Engineering , ASCE, pp. 1165-1177, dated September 2006.
California Building Standards Commission, 2022, Ca lifornia Building Code, California Code of Regulations Title 24, Volumes 1 and 2, dated July 2022.
California Department of Transportation (Caltrans), 2020, Highway Design Manual, Updated March 20, 2020.
California Department of Conservation, Division of Mines and Geology (CDMG), 1998, Seismic Hazard Zone Report for the Mt. Wilson 7.5-Minute Quadrangle, Los Angeles County, California, Seismic Hazard Zone Report 030, revised January 13, 2006.
________, 1999, State of California Seismic Hazard Zones, Mt. Wilson Quadrangle, Official Map, scale:
1:24,000, dated March 25, 1999.
California Geological Survey (CGS), 2008, Califo rnia Geological Survey Special Publication 117A:
Guidelines for Evaluating and Mitigating Seismic Hazards in California.
_______, 2017, Earthquake Zones of Required Investig ation, Mount Wilson Quadrangle, dated June 15, 2017.
________, 2018, Special Publication 42: Earthquake Fault Zones, A Guide for Government Agencies, Property Owners/Developers, and Geoscience Practitioners for Assessing Fault Rupture Hazards in California, Revised 2018.
________, 2025, Earthquake Zones of Required Investigation website: CGS Earthquake Zones (ca.gov) ; retrieved June 24, 2025.
County of Los Angeles, 2021, Guidelines for Geot echnical Investigation an d Reporting Low Impact Development Stormwater Infiltration, GS200.1, dated June 30, 2021.
Project No. 25041-01 A-2 June 26, 2025
Diblee, et al, 1998, Geologic Map of the Mount Wilson & Azusa Quadrangles, Los Angeles County, California, Dibblee Geology Center Map #DF-67, Last edited 2010.
Historic Aerials, 2025, vi ewed June 24, 2025, Aerial Maps from 1952 to 2022 https://www.historicaerials.com/.
KTGY, 2025, Conceptual Site Plan, Option 5c, Colorado Place, Arcadia, California, dated May 14, 2025.
Lew, et al, 2010, Seismic Earth Pr essures on Deep Basements, Stru ctural Engineers Association of California (SEAOC) Convention Proceedings.
Pradel, Daniel, 1998, Procedure to evaluate earthquake-induced settlement in dry sandy soils, Journal of Geotechnical and Geoenvironmental Engineering, Volume 124(4), pp. 364-368, dated April and October 1998.
Structural Engineers Association of California (SEAOC), 2025, Seismic Design Maps, Retrieved June 24, 2025, from https://seismicmaps.org/
United States Geological Survey (USGS), 2014, Unif ied Hazard Tool, Dynamic: Conterminous U.S. 2014 (update)(v4.2.0), Retrieved June 24, 2025, from:
https://earthquake.usgs.gov/hazards/interactive/
Appendix B
Field Exploration Logs
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Appendix C
Laboratory Test Results
Project No. 25041-01 C-1 June 2025
APPENDIX C
Laboratory Testing Procedures and Test Results
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Sample
Location
Expansion
Index
Expansion
Potential*
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Sample
Location
Description % Passing # 200
Sieve
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APPENDIX C (Cont’d)
Laboratory Testing Procedures and Test Results
Project No. 25041-01 C-2 June 2025
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Sample
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Liquid Limit
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Plastic Limit
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Plasticity Index
(%)
USCS Soil
Classification
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Sample
Location Sample Description
Maximum
Dry Density
(pcf)
Optimum
Moisture
Content (%)
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APPENDIX C (Cont’d)
Laboratory Testing Procedures and Test Results
Project No. 25041-01 C-3 June 2025
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Sample
Location
Sulfate Content
(ppm)
Sulfate Exposure
Class *
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Sample Location Chloride Content, ppm
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Location pH Minimum Resistivity
(ohms-cm)
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Project Name: Tested By: GB/JD Date: 04/17/25
Project No.: Checked By: J. Ward Date: 04/30/25
Boring No.: Depth (ft.):
Sample No.: Sample Type:
Soil Identification:
Sample Diameter (in.): 2.415
Sample Thickness (in.): 1.000
Weight of Sample + ring (g): 191.83
Weight of Ring (g): 44.27
Height after consol. (in.): 0.9688
Before Test
Wt. of Wet Sample+Cont. (g): 177.47
Wt. of Dry Sample+Cont. (g): 169.32
Weight of Container (g): 39.71
Initial Moisture Content (%) 6.3
Initial Dry Density (pcf) 115.5
Initial Saturation (%): 37
Initial Vertical Reading (in.) 0.1162
After Test
Wt. of Wet Sample+Cont. (g): 256.34
Wt. of Dry Sample+Cont. (g): 237.37
Weight of Container (g): 57.28
Final Moisture Content (%) 13.97
Final Dry Density (pcf): 116.6
Final Saturation (%): 85
Final Vertical Reading (in.) 0.1507
Specific Gravity (assumed): 2.70
Water Density (pcf): 62.43
0.10 0.1165 0.9997 0.00 0.03 0.459 0.03
0.25 0.1190 0.9972 0.05 0.28 0.457 0.23
0.50 0.1209 0.9953 0.12 0.47 0.455 0.35
1.00 0.1247 0.9916 0.21 0.84 0.451 0.63
1.00 0.1250 0.9912 0.21 0.88 0.450 0.67
2.00 0.1286 0.9877 0.31 1.24 0.446 0.92
4.00 0.1346 0.9816 0.41 1.84 0.439 1.43
8.00 0.1437 0.9726 0.52 2.75 0.427 2.23
16.00 0.1603 0.9560 0.64 4.41 0.405 3.77
8.00 0.1589 0.9573 0.59 4.27 0.406 3.68
4.00 0.1573 0.9590 0.53 4.11 0.408 3.58
1.00 0.1531 0.9631 0.39 3.69 0.412 3.30
0.50 0.1507 0.9655 0.33 3.45 0.41 3.120
ONE-DIMENSIONAL CONSOLIDATION
ASTM D 2435
25041-01
Arcadia
Deformation
% of Sample
Thickness
Final
Reading
(in.)
PROPERTIES of SOILS
Ring
Void
Ratio
Pressure
(p)
(ksf) Time Dial Rdgs.
(in.)Date
Apparent
Thickness
(in.)
Load
Compliance
(%)
HS-2
R-2
Square
Root of
Time
Corrected
Deforma-
tion (%)
Olive brown silty sand (SM)
Time Readings
Elapsed
Time (min)
7.5 0.400
0.410
0.420
0.430
0.440
0.450
0.460
0.470
0.10 1.00 10.00
100.
Void Ratio
Pressure, p (ksf)
Inundate with
Tap water
Consol HS-2, R-2 @ 7.5
Initial Final Initial Final Initial Final Initial Final Soil Identification:
Boring
No.
Sample
No.
Depth
(ft.)
Moisture
Content (%)
ONE-DIMENSIONAL CONSOLIDATION
PROPERTIES of SOILS
ASTM D 2435
14.0 116.6HS-2 R-2 6.3
Olive brown silty sand (SM)
Project No.:
Arcadia
04-25
25041-01
Time Readings
0.414 37 85115.5
Degree of
Saturation (%)Dry Density (pcf)
0.460
Void Ratio
7.5 0.0000
0.2000
0.4000
0.6000
0.8000
1.0000
1.2000
0.1 1.0
Deformation Dial Reading (in.)
Log of Time (min.)
0.00 0.50
1.00 1.50
2.00 2.50
3.00 3.50
4.00 0.10 1.00 10.00 100.00
Deformation (%)
Pressure, p (ksf)
0.0000
0.2000
0.4000
0.6000
0.8000
1.0000
1.2000
0.0 10.0
Square Root of Time (min.1/2)
Inundate with
Tap water
Project Name: Arcadia Tested By: G. Bathala Date: 04/23/25 Project No.: 25041-01 Checked By: J. Ward Date: 04/30/25 Boring No.: Sample Type: 90% Remold
Sample No.: Depth (ft.): 1-5
Soil Identification:
2.415 2.415 2.415
1.000 1.000 1.000
199.35 196.45 199.23
45.39 42.26 44.97
Before Shearing
218.81 218.81 218.81
207.98 207.98 207.98
77.77 77.77 77.77
0.2626 0.2739 0.0000
0.2713 0.2884 -0.0245
After Shearing
225.12 217.32 209.92
207.21 199.34 192.80
67.40 59.14 52.64
2.70 2.70 2.70
62.43 62.43 62.43
HS-2
Dark brown silty sand (SM)
Sample Diameter(in):
Weight of Wet Sample+Cont.(gm):
Vertical Rdg.(in): Final
Vertical Rdg.(in): Initial
Sample Thickness(in.):
Weight of Sample + ring(gm):
B-1
',5(&76+($57(67
&RQVROLGDWHG'UDLQHG$670'
Water Density(pcf):
Specific Gravity (Assumed):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Ring(gm):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Wet Sample+Cont.(gm):
DS HS-2, B-1 @ 1-5
Normal Stress (kip/ft²)
Peak Shear Stress (kip/ft²)
Shear Stress @ End of Test (ksf)
Deformation Rate (in./min.)
Initial Sample Height (in.)
Diameter (in.)
Initial Moisture Content (%)
Dry Density (pcf)
Saturation (%)
Soil Height Before Shearing (in.)
Final Moisture Content (%)
04-25
Project No.: 25041-01
Sample Type:
90% Remold
Dark brown silty sand (SM)
52.7 0.9913
12.8 Arcadia',5(&76+($57(675(68/76
&RQVROLGDWHG'UDLQHG$670'
53.1 0.9755
12.2 1.000
0.912
0.777
0.0033
1.000
2.415
1.000
2.415
2.000
1.625
1.449
0.0033
4.000
3.122
2.804
0.0033
53.0 0.9855
12.8 Soil Identification:
8.32 118.4
8.32 118.2 118.4
1.000
2.415
8.32 Boring No.
Sample No.
Depth (ft)
HS-2
B-1
1-5
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Project Name: MWIG - Arcadia Tested By: J. Domingo Date: 06/04/25 Project No.: 25041-01 Checked By: J. Ward Date: 06/12/25 Boring No.: Sample Type: Ring
Sample No.: Depth (ft.): 7.5
Soil Identification:
2.415 2.415 2.415
1.000 1.000 1.000
175.86 176.56 178.72
45.03 45.39 42.81
Before Shearing
172.82 172.82 172.82
165.19 165.19 165.19
67.11 67.11 67.11
0.2737 0.2863 0.0000
0.2903 0.3168 -0.0573
After Shearing
193.66 199.08 201.22
166.85 174.96 180.45
49.74 56.35 57.05
2.70 2.70 2.70
62.43 62.43 62.43
',5(&76+($57(67
&RQVROLGDWHG'UDLQHG$670'
Water Density(pcf):
Specific Gravity (Assumed):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Ring(gm):
Weight of Container(gm):
Weight of Dry Sample+Cont.(gm):
Weight of Wet Sample+Cont.(gm):
HS-4
Brown silty sand with gravel (SM)g
Sample Diameter(in):
Weight of Wet Sample+Cont.(gm):
Vertical Rdg.(in): Final
Vertical Rdg.(in): Initial
Sample Thickness(in.):
Weight of Sample + ring(gm):
R-2
DS HS-4, R-2 @ 7.5
Normal Stress (kip/ft²)
Peak Shear Stress (kip/ft²)
Shear Stress @ End of Test (ksf)
Deformation Rate (in./min.)
Initial Sample Height (in.)
Diameter (in.)
Initial Moisture Content (%)
Dry Density (pcf)
Saturation (%)
Soil Height Before Shearing (in.)
Final Moisture Content (%)
104.9
1.000
2.415
7.78 Boring No.
Sample No.
Depth (ft)
HS-4
R-2
7.5 31.6
0.9695
20.3 Soil Identification:
7.78 101.2
7.78 101.0
1.185
0.0033
4.000
2.842
2.836
0.0033
1.000
0.742
0.732
0.0033
1.000
2.415
1.000
2.415
2.000
1.191
31.4 0.9834
22.9 MWIG - Arcadia
',5(&76+($57(675(68/76
&RQVROLGDWHG'UDLQHG$670'
34.6 0.9427
16.8 06-25
Project No.: 25041-01
Sample Type:
Ring
Brown silty sand with gravel
(SM)g
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Appendix D
Infiltration Test Results
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ͳͲǣʹͺ ͳͲǣ͵ͺ ͳͲǤͲ ͳͳǤͻͶ ͳ͵Ǥ ͳǤͺ͵ Ǥ Ǥͺ
ͺ ͳͲǣͶͳ ͳͲǣͷͳ ͳͲǤͲ ͳͳǤͻ͵ ͳ͵Ǥͺ ͳǤͺͷ Ǥͺ Ǥͻ
ͻ ͳͲǣͷͶ ͳͳǣͲͶ ͳͲǤͲ ͳͳǤͻʹ ͳ͵Ǥͺʹ ͳǤͻͲ ǤͺͲ ǤͲ
ͳͲ ͳͳǣͲ ͳͳǣͳ ͳͲǤͲ ͳͳǤͻͺ ͳ͵Ǥͺͳ ͳǤͺ͵ Ǥ Ǥͻ
ͳͳ ͳͳǣʹͲ ͳͳǣ͵Ͳ ͳͲǤͲ ͳͳǤͻʹ ͳ͵Ǥͺ ͳǤͺͺ ǤͺͲ Ǥͻ
ͳʹ ͳͳǣ͵͵ ͳͳǣͶ͵ ͳͲǤͲ ͳͳǤͻʹ ͳ͵Ǥͺ ͳǤͺͺ ǤͺͲ Ǥͻ
Ǥͻ
ǣ ǣ
ȋ
Ȍ
ǡ
ͳ͵ͳ
ǡǡͻʹʹǤȋͻͶͻȌ͵ͻǦͳͶͳ
ǣ
Ǧ
ǣ ʹͷͲͶͳǦͲͳ
ǣ ͶȀͳͷȀʹͲʹͷ
Ǧʹ
ȋȌȗǣ ȋȌǣ
ȋ
Ȍǣ ȋȌǣ
ȋ
Ȍǣ ȋȌǣ
ȗ
ǣȀʹʹȀʹͲʹ͵
͵Ͳ
Ǥ
ȋʹͶǣ
Ȍ
ȋʹͶǣ
Ȍ
ǡ
ȋȌ
ǡ
ȋȌ
ǡ
ȋȌ
ǡ
ȋȌ
ḭ̑ʹȌ
ȋȀȌ
ǣͲȀʹͲʹͳ
>ŽĐĂƚŝŽŶ͗
dĞƐƚŚŽůĞĚŝŵĞŶƐŝŽŶƐ;ŝĨĐŝƌĐƵůĂƌͿ
ϭϱ
ϴ
ϯ
WƌĞͲ^ŽĂŬͬWƌĞͲdĞƐƚ
EŽ͘ ^ƚĂƌƚdŝŵĞ
;Ϯϰ͗,ZͿ
^ƚŽƉdŝŵĞ
;Ϯϰ͗,ZͿ
dŝŵĞ/ŶƚĞƌǀĂů
;ŵŝŶͿ
/ŶŝƚŝĂůĞƉƚŚƚŽ
tĂƚĞƌ;ĨĞĞƚͿ
&ŝŶĂůĞƉƚŚ
ƚŽtĂƚĞƌ;ĨĞĞƚͿ
dŽƚĂůŚĂŶŐĞ
ŝŶtĂƚĞƌ>ĞǀĞů
;ĨĞĞƚͿ
WƌĞͲdĞƐƚ ϳ͗Ϯϯ ϳ͗ϱϯ ϯϬ͘Ϭ ϭϯ͘ϵϵ ϭϰ͘ϳϵ Ϭ͘ϴ
DĂŝŶdĞƐƚĂƚĂ
ϭ ϳ͗ϱϴ ϴ͗Ϯϴ ϯϬ͘Ϭ ϭϭ͘ϵϭ ϭϰ͘ϯϴ Ϯ͘ϰϳ ϲ͘ϴϮ ϯ͘Ϭ
Ϯ ϴ͗ϯϮ ϴ͗ϰϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϱϵ ϭ͘ϲϯ ϲ͘ϳϮ ϲ͘ϭ
ϯ ϴ͗ϰϱ ϴ͗ϱϱ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϳ ϭ͘ϱϮ ϲ͘ϳϰ ϱ͘ϳ
ϰ ϴ͗ϱϳ ϵ͗Ϭϳ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϰϰ ϭ͘ϰϴ ϲ͘ϳϮ ϱ͘ϱ
ϱ ϵ͗Ϭϵ ϵ͗ϭϵ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϵ ϭ͘ϱϰ ϲ͘ϳϰ ϱ͘ϳ
ϲ ϵ͗ϮϮ ϵ͗ϯϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϰϭ ϭ͘ϰϱ ϲ͘ϳϮ ϱ͘ϰ
ϳ ϵ͗ϯϰ ϵ͗ϰϰ ϭϬ͘Ϭ ϭϭ͘ϵϵ ϭϯ͘ϯϴ ϭ͘ϯϵ ϲ͘ϲϱ ϱ͘ϯ
ϴ ϵ͗ϰϱ ϵ͗ϱϱ ϭϬ͘Ϭ ϭϭ͘ϵϴ ϭϯ͘ϰϰ ϭ͘ϰϲ ϲ͘ϲϳ ϱ͘ϱ
ϵ ϵ͗ϱϴ ϭϬ͗Ϭϴ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϳ ϭ͘ϱϮ ϲ͘ϳϰ ϱ͘ϳ
ϭϬ ϭϬ͗ϭϮ ϭϬ͗ϮϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϰϮ ϭ͘ϰϲ ϲ͘ϳϮ ϱ͘ϱ
ϭϭ ϭϬ͗Ϯϰ ϭϬ͗ϯϰ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰϬ ϭ͘ϰϱ ϲ͘ϳϰ ϱ͘ϰ
ϭϮ ϭϬ͗ϯϲ ϭϬ͗ϰϲ ϭϬ͘Ϭ ϭϭ͘ϵϭ ϭϯ͘ϯϮ ϭ͘ϰϭ ϲ͘ϴϮ ϱ͘Ϯ
ϭϯ ϭϬ͗ϱϵ ϭϭ͗Ϭϵ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϯ͘ϯϵ ϭ͘ϰϮ ϲ͘ϳϬ ϱ͘ϯ
ϭϰ ϭϭ͗ϭϮ ϭϭ͗ϮϮ ϭϬ͘Ϭ ϭϭ͘ϵϲ ϭϯ͘ϯϳ ϭ͘ϰϭ ϲ͘ϳϮ ϱ͘ϯ
ϭϱ ϭϭ͗Ϯϰ ϭϭ͗ϯϰ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϯ͘ϯϱ ϭ͘ϯϴ ϲ͘ϳϬ ϱ͘Ϯ
ϭϲ ϭϭ͗ϯϲ ϭϭ͗ϰϲ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϰ ϭ͘ϰϱ ϲ͘ϳϰ ϱ͘ϰ
ϱ͘ϯ
d
d
^ŬĞƚĐŚ͗ EŽƚĞƐ͗
ZĂǁ
WĞƌĐŽůĂƚŝŽŶ
ZĂƚĞ;ŝŶͬŚƌͿ
/ŶĨŝůƚƌĂƚŝŽŶZĂƚĞ
&ĂĐƚŽƌŽĨ^ĂĨĞƚLJ
ĞƐŝŐŶ/ŶĨŝůƚƌĂƚŝŽŶZĂƚĞ
ĂƐĞĚŽŶ'ƵŝĚĞůŝŶĞƐĨƌŽŵ͗>ŽƵŶƚLJĚĂƚĞĚϬϲͬϮϬϮϭ
^ƉƌĞĂĚƐŚĞĞƚZĞǀŝƐĞĚŽŶ͗ϲͬϮϮͬϮϬϮϯ
ŽŵŵĞŶƚƐ
dƌŝĂůEŽ͘ ^ƚĂƌƚdŝŵĞ
;Ϯϰ͗,ZͿ
^ƚŽƉdŝŵĞ
;Ϯϰ͗,ZͿ
dŝŵĞ/ŶƚĞƌǀĂů͕
Δƚ;ŵŝŶͿ
/ŶŝƚŝĂůĞƉƚŚƚŽ
tĂƚĞƌ͕Ž
;ĨĞĞƚͿ
&ŝŶĂůĞƉƚŚƚŽ
tĂƚĞƌ͕Ĩ
;ĨĞĞƚͿ
ŚĂŶŐĞŝŶ
tĂƚĞƌ>ĞǀĞů͕
Δ;ĨĞĞƚͿ
^ƵƌĨĂĐĞƌĞĂŽĨ
dĞƐƚ^ĞĐƚŝŽŶ
;ĨĞĞƚΔϮͿ
ΎŵĞĂƐƵƌĞĚĂƚƚŝŵĞŽĨƚĞƐƚ
ŽƌŝŶŐĞƉƚŚ;ĨĞĞƚͿΎ͗ WŝƚĞƉƚŚ;ĨĞĞƚͿ͗
ŽƌŝŶŐŝĂŵĞƚĞƌ;ŝŶĐŚĞƐͿ͗ Wŝƚ>ĞŶŐƚŚ;ĨĞĞƚͿ͗
WŝƉĞŝĂŵĞƚĞƌ;ŝŶĐŚĞƐͿ͗ WŝƚƌĞĂĚƚŚ;ĨĞĞƚͿ͗
ĂƚĞ͗ ϱͬϮϵͬϮϬϮϱ
/Ͳϯ
dĞƐƚƉŝƚĚŝŵĞŶƐŝŽŶƐ;ŝĨƌĞĐƚĂŶŐƵůĂƌͿ
/ŶĨŝůƚƌĂƚŝŽŶdĞƐƚĂƚĂ^ŚĞĞƚ
>''ĞŽƚĞĐŚŶŝĐĂů͕/ŶĐ
ϭϯϭĂůůĞ/ŐůĞƐŝĂ^ƵŝƚĞ͕^ĂŶůĞŵĞŶƚĞ͕ϵϮϲϳϮƚĞů͘;ϵϰϵͿϯϲϵͲϲϭϰϭ WƌŽũĞĐƚEĂŵĞ͗ Dt/'ͲƌĐĂĚŝĂ
WƌŽũĞĐƚEƵŵďĞƌ͗ ϮϱϬϰϭͲϬϭ
>ŽĐĂƚŝŽŶ͗
dĞƐƚŚŽůĞĚŝŵĞŶƐŝŽŶƐ;ŝĨĐŝƌĐƵůĂƌͿ
ϭϱ
ϴ
ϯ
WƌĞͲ^ŽĂŬͬWƌĞͲdĞƐƚ
EŽ͘ ^ƚĂƌƚdŝŵĞ
;Ϯϰ͗,ZͿ
^ƚŽƉdŝŵĞ
;Ϯϰ͗,ZͿ
dŝŵĞ/ŶƚĞƌǀĂů
;ŵŝŶͿ
/ŶŝƚŝĂůĞƉƚŚƚŽ
tĂƚĞƌ;ĨĞĞƚͿ
&ŝŶĂůĞƉƚŚ
ƚŽtĂƚĞƌ;ĨĞĞƚͿ
dŽƚĂůŚĂŶŐĞ
ŝŶtĂƚĞƌ>ĞǀĞů
;ĨĞĞƚͿ
WƌĞͲdĞƐƚ ϴ͗Ϭϳ ϴ͗ϯϳ ϯϬ͘Ϭ ϭϮ͘ϭϱ ϭϰ͘Ϯ Ϯ͘Ϭϱ
DĂŝŶdĞƐƚĂƚĂ
ϭ ϴ͗ϯϵ ϴ͗ϰϵ ϭϬ͘Ϭ ϭϭ͘ϰϰ ϭϮ͘ϵϰ ϭ͘ϱϬ ϳ͘ϴϭ ϰ͘ϴ
Ϯ ϴ͗ϱϬ ϵ͗ϬϬ ϭϬ͘Ϭ ϭϭ͘ϵϯ ϭϯ͘Ϭϵ ϭ͘ϭϲ ϲ͘ϳϴ ϰ͘ϯ
ϯ ϵ͗ϬϮ ϵ͗ϭϮ ϭϬ͘Ϭ ϭϭ͘ϴϱ ϭϮ͘ϵϮ ϭ͘Ϭϳ ϲ͘ϵϱ ϯ͘ϵ
ϰ ϵ͗ϭϰ ϵ͗ϱϬ ϯϲ͘Ϭ ϭϭ͘ϵϱ ϭϰ͘Ϭϳ Ϯ͘ϭϮ ϲ͘ϳϰ Ϯ͘Ϯ
ϱ ϵ͗ϱϯ ϭϬ͗Ϭϯ ϭϬ͘Ϭ ϭϭ͘ϴϬ ϭϮ͘ϵϴ ϭ͘ϭϴ ϳ͘Ϭϱ ϰ͘Ϯ
ϲ ϭϬ͗Ϭϱ ϭϬ͗ϭϱ ϭϬ͘Ϭ ϭϭ͘ϵϯ ϭϯ͘ϬϬ ϭ͘Ϭϳ ϲ͘ϳϴ ϰ͘Ϭ
ϳ ϭϬ͗ϭϴ ϭϬ͗Ϯϴ ϭϬ͘Ϭ ϭϭ͘ϵϴ ϭϯ͘ϭϬ ϭ͘ϭϮ ϲ͘ϲϳ ϰ͘Ϯ
ϴ ϭϬ͗ϯϮ ϭϬ͗ϰϮ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϯ͘ϭϮ ϭ͘ϭϱ ϲ͘ϳϬ ϰ͘ϯ
ϵ ϭϭ͗Ϭϲ ϭϭ͗ϭϲ ϭϬ͘Ϭ ϭϭ͘ϴϮ ϭϮ͘ϴϮ ϭ͘ϬϬ ϳ͘Ϭϭ ϯ͘ϲ
ϭϬ ϭϭ͗ϭϴ ϭϭ͗Ϯϴ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϮ͘ϴϲ Ϭ͘ϵϭ ϲ͘ϳϰ ϯ͘ϰ
ϭϭ ϭϭ͗ϯϬ ϭϭ͗ϰϬ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϮ͘ϵϵ ϭ͘ϬϮ ϲ͘ϳϬ ϯ͘ϴ
ϭϮ ϭϭ͗ϰϯ ϭϭ͗ϱϯ ϭϬ͘Ϭ ϭϭ͘ϵϴ ϭϯ͘Ϭϰ ϭ͘Ϭϲ ϲ͘ϲϳ ϰ͘Ϭ
ϭϯ ϭϭ͗ϱϳ ϭϮ͗Ϭϳ ϭϬ͘Ϭ ϭϭ͘ϵϯ ϭϯ͘Ϭϱ ϭ͘ϭϮ ϲ͘ϳϴ ϰ͘Ϯ
ϭϰ ϭϮ͗Ϭϵ ϭϮ͗ϭϵ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϭϬ ϭ͘ϭϱ ϲ͘ϳϰ ϰ͘ϯ
ϭϱ ϭϮ͗Ϯϱ ϭϮ͗ϯϱ ϭϬ͘Ϭ ϭϭ͘ϵϳ ϭϯ͘ϭϴ ϭ͘Ϯϭ ϲ͘ϳϬ ϰ͘ϱ
ϭϲ ϭϮ͗ϯϴ ϭϮ͗ϰϴ ϭϬ͘Ϭ ϭϭ͘ϵϱ ϭϯ͘ϭϰ ϭ͘ϭϵ ϲ͘ϳϰ ϰ͘ϰ
ϰ͘ϰ
d
d
^ŬĞƚĐŚ͗ EŽƚĞƐ͗
ZĂǁ
WĞƌĐŽůĂƚŝŽŶ
ZĂƚĞ;ŝŶͬŚƌͿ
/ŶĨŝůƚƌĂƚŝŽŶZĂƚĞ
&ĂĐƚŽƌŽĨ^ĂĨĞƚLJ
ĞƐŝŐŶ/ŶĨŝůƚƌĂƚŝŽŶZĂƚĞ
ĂƐĞĚŽŶ'ƵŝĚĞůŝŶĞƐĨƌŽŵ͗>ŽƵŶƚLJĚĂƚĞĚϬϲͬϮϬϮϭ
^ƉƌĞĂĚƐŚĞĞƚZĞǀŝƐĞĚŽŶ͗ϲͬϮϮͬϮϬϮϯ
ŽŵŵĞŶƚƐ
dƌŝĂůEŽ͘ ^ƚĂƌƚdŝŵĞ
;Ϯϰ͗,ZͿ
^ƚŽƉdŝŵĞ
;Ϯϰ͗,ZͿ
dŝŵĞ/ŶƚĞƌǀĂů͕
Δƚ;ŵŝŶͿ
/ŶŝƚŝĂůĞƉƚŚƚŽ
tĂƚĞƌ͕Ž
;ĨĞĞƚͿ
&ŝŶĂůĞƉƚŚƚŽ
tĂƚĞƌ͕Ĩ
;ĨĞĞƚͿ
ŚĂŶŐĞŝŶ
tĂƚĞƌ>ĞǀĞů͕
Δ;ĨĞĞƚͿ
^ƵƌĨĂĐĞƌĞĂŽĨ
dĞƐƚ^ĞĐƚŝŽŶ
;ĨĞĞƚΔϮͿ
ΎŵĞĂƐƵƌĞĚĂƚƚŝŵĞŽĨƚĞƐƚ
ŽƌŝŶŐĞƉƚŚ;ĨĞĞƚͿΎ͗ WŝƚĞƉƚŚ;ĨĞĞƚͿ͗
ŽƌŝŶŐŝĂŵĞƚĞƌ;ŝŶĐŚĞƐͿ͗ Wŝƚ>ĞŶŐƚŚ;ĨĞĞƚͿ͗
WŝƉĞŝĂŵĞƚĞƌ;ŝŶĐŚĞƐͿ͗ WŝƚƌĞĂĚƚŚ;ĨĞĞƚͿ͗
ĂƚĞ͗ ϱͬϮϵͬϮϬϮϱ
/Ͳϰ
dĞƐƚƉŝƚĚŝŵĞŶƐŝŽŶƐ;ŝĨƌĞĐƚĂŶŐƵůĂƌͿ
/ŶĨŝůƚƌĂƚŝŽŶdĞƐƚĂƚĂ^ŚĞĞƚ
>''ĞŽƚĞĐŚŶŝĐĂů͕/ŶĐ
ϭϯϭĂůůĞ/ŐůĞƐŝĂ^ƵŝƚĞ͕^ĂŶůĞŵĞŶƚĞ͕ϵϮϲϳϮƚĞů͘;ϵϰϵͿϯϲϵͲϲϭϰϭ WƌŽũĞĐƚEĂŵĞ͗ Dt/'ͲƌĐĂĚŝĂ
WƌŽũĞĐƚEƵŵďĞƌ͗ ϮϱϬϰϭͲϬϭ
Appendix E
General Earthwork & Grading Specifications
for Rough Grading
General Earthwork and Grading Specifications for Rough Grading
1.0 General
1.1 Intent
7KHVH *HQHUDO (DUWKZRUN DQG *UDGLQJ 6SHFLILFDWLRQV DUH IRU WKH JUDGLQJ DQGHDUWKZRUN VKRZQRQWKHDSSURYHGJUDGLQJSODQ
V
DQGRULQGLFDWHGLQWKHJHRWHFKQLFDOUHSRUW
V
7KHVH
6SHFLILFDWLRQV DUH D SDUW RI WKH UHFRPPHQGDWLRQV FRQWDLQHG LQ WKHJHRWHFKQLFDOUHSRUW V
,Q
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1.2 The Geotechnical Consultant of Record
3ULRUWRFRPPHQFHPHQWRIZRUNWKHRZQHUVKDOOHPSOR\D TXDOLILHG*HRWHFKQLFDO&RQVXOWDQW RI 5HFRUG
*HRWHFKQLFDO &RQVXOWDQW
7KH *HRWHFKQLFDO &RQVXOWDQW VKDOO EH UHVSRQVLEOH IRU UHYLHZLQJWKH DSSURYHGJHRWHFKQLFDOUHSRUW
V
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&RQWUDFWRU
DQGVFKHGXOHVXIILFLHQWSHUVRQQHOWR
SHUIRUPWKHDSSURSULDWHOHYHORIREVHUYDWLRQPDSSLQJDQGFRPSDFWLRQWHVWLQJ
'XULQJ WKH JUDGLQJ DQG HDUWKZRUN RSHUDWLRQV WKH *HRWHFKQLFDO &RQVXOWDQW VKDOO REVHUYH PDSDQGGRFXPHQWWKHVXEVXUIDFHH[SRVXUHVWRYHULI\WKHJHRWHFKQLFDOGHVLJQDVVXPSWLRQV,I WKH REVHUYHG FRQGLWLRQV DUH IRXQG WR EH VLJQLILFDQWO\ GLIIHUHQW WKDQ WKH LQWHUSUHWHG DVVXPSWLRQV GXULQJ WKH GHVLJQ SKDVH WKH *HRWHFKQLFDO &RQVXOWDQW VKDOO LQIRUP WKH RZQHU UHFRPPHQG DSSURSULDWH FKDQJHV LQ GHVLJQ WR DFFRPPRGDWH WKH REVHUYHG FRQGLWLRQV DQG QRWLI\WKHUHYLHZDJHQF\ZKHUHUHTXLUHG
7KH *HRWHFKQLFDO &RQVXOWDQW VKDOO REVHUYH WKH PRLVWXUHFRQGLWLRQLQJDQG SURFHVVLQJ RI WKH VXEJUDGHDQGILOOPDWHULDOVDQGSHUIRUPUHODWLYHFRPSDFWLRQWHVWLQJRIILOOWRFRQILUPWKDWWKH DWWDLQHGOHYHORIFRPSDFWLRQLVEHLQJDFFRPSOLVKHGDVVSHFLILHG7KH*HRWHFKQLFDO&RQVXOWDQW VKDOOSURYLGHWKHWHVWUHVXOWVWRWKHRZQHUDQGWKH&RQWUDFWRURQDURXWLQHDQGIUHTXHQWEDVLV
1.3 The Earthwork Contractor
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PROJECT: DATE: 6/18/2025
LOCATION: MAIN SIZE:
TESTED BY: TIME:
WATER ATLAS PRESSURE: 76
GAUGE
JUCTION #
ORIFACE DIAMETER: (in)
STATIC PRESSURE: (psi)
RESIDUAL PRESSURE: (psi)
CALCULATED FLOW (gpm)
FLOW @ 20 PSI (gpm)
REMARKS:
Disclaimer:
500.00
3,424.15
SIMULATED FLOW TEST FROM WATER MODEL.
This information is furnished as a courtesy and shall not constitue any obligation on the part of the City of Arcadia to supply water at any specific pressure, or in any specific quantity for domestic or fire protection use.
76.62 73.35
Tiffany Lee
FLOW TEST RESULTS
FLOW FIRE HYDRANT
408FH005
City of Arcadia
Public Works Services Department
Hydraulic Flow Test Summary
201 Colorado Pl
201 Colorado Pl 8" CI
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ES-F-856ST
MasterSeries® 856ST
Double Check Detector Backflow
Prevention Assemblies
Size: 21⁄2" - 10" (65mm - 250mm)
Model 856ST Double Check Detector Assembly
The FEBCO MasterSeries 856ST Double Check Detector Assemblies are designed to protect drinking water supplies from dangerous cross-con- nections in accordance with national plumbing codes and water authority requirements for non-health hazard non-potable service applications such as irrigation, fire line, or industrial processing. This Backflow Assembly is primar- ily used for protection of drinking water systems and fire sprinkler systems, where Local Governing Code mandates protection from non-potable quality water being pumped or siphoned back into the potable water system.
Features
Main Valve:
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Specifications
5IF'&#$0.BTUFS4FSJFT45%PVCMF$IFDL%FUFDUPS7BMWF"TTFNCMZTIBMM be installed on the potable water supply and at each point of cross-connec- tion to protect against possible backpressure and backsiphonage conditions for non-health hazard (i.e., pollutant) applications. The assembly shall consist PGBNBJOMJOFWBMWFCPEZDPNQPTFEPGUXP
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Servicing of both check modules does not require any special tools and are accessed through independent top entry covers. This assembly shall be fitted XJUIBQQSPWFE6-'.JOMFUPVUMFUSFTJMJFOUTFBUFETIVUPGGWBMWF TBOEDPOUBJO GPVS
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The bypass line is designed to detect leaks or unauthorized water usage of the water system while protecting against possible backpressure and back- siphonage conditions for non-health hazard (i.e., pollutant) application. Flow and pressure loss performance parameters shall meet the requirements of "88"4UBOEBSE$
NOTICE
The information contained herein is not intended to replace the full prod- uct installation and safety information available or the experience of a trained product installer. You are required to thoroughly read all installation instructions and product safety information before beginning the installa- tion of this product.
SPECIFICATION SHEET
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Before installing standard material product, consult your local water authority, building and plumbing codes.
WARNING!
FEBCO product specifications in U.S. customary units and metric are approximate and are provided for reference only. For precis e measurements, please contact FEBCO Technical Service. FEBCO reserves the right to change or modify product design, construction, specifications, or materials without prior notice and with out incurring any obligation to make such changes and modifications on FEBCO products previously or subsequently sold.
Job Name –––––––––––––––––––––––––––––––––––––––––––– Contractor –––––––––––––––––––––––––––––––––––––––––––– Job Location ––––––––––––––––––––––––––––––––––––––––– Approval –––––––––––––––––––––––––––––––––––––––––––––– Engineer ––––––––––––––––––––––––––––––––––––––––––––– Contractor’s P .O. No. ––––––––––––––––––––––––––––––––––– Approval ––––––––––––––––––––––––––––––––––––––––––––– Representative –––––––––––––––––––––––––––––––––––––––– Approvals
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Example Ordering Descriptions:
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Test Cock #3
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Assembly
First Spring
Assembly
Second Spring
Assembly
Second Check
Assembly
1048
****
Dimensions & Weights
Below are the nominal dimensions and physical weights for the Model 856ST TJ[F⁄UISPVHI"MMPXBODFTNVTUCFNBEFGPSOPSNBMNBOVGBDUVS- JOHUPMFSBODFT1MFBTFWJTJUPVSXFCTJUFUPEPXOMPBEBDPQZPG UIJTQSPEVDUT JOTUBMMBUJPOJOTUSVDUJPOT
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information.
Model 856ST Assemblies
SIZE DIMENSIONS WEIGHT***
A B C E** F G H OSY
in. in. mm in. mm in. mm in. mm in. mm in. mm in. mm lbs. kg. 21⁄2 403⁄4 1035 25 1⁄2 648 10 254 16 3⁄8 416 4 1⁄2 114 7 1⁄8 181 13 3⁄8 340 245 1 1 1 34 1 7⁄8 1064 25 5⁄8 651 10 254 22 1⁄7 565 4 1⁄2 114 7 3⁄8 187 13 3⁄8 340 271 123 44 6 1⁄4 1 175 28 71 1 10 1⁄8 257 23 1⁄4 591 5 1⁄2 140 8 1⁄8 206 14 356 338 153 6 56 1422 34 3⁄4 883 12 3⁄4 324 30 1⁄8 765 6 1⁄2 165 9 7⁄8 251 15 381 515 234 8 65 1651 41 3⁄4 1061 15 5⁄8 397 37 3⁄4 959 7 178 1 1 1⁄8 283 15 3⁄4 400 826 375 10 72 5⁄8 1845 46 3⁄8 117 8 15 5⁄8 397 48 1219 9 229 12 3⁄8 314 15 3⁄4 400 1234 560 ** Indicates nominal dimensions with OSY Gate Valves (Full Open Position) *** Indicates weight of complete Backflow Assemblies with specified Gate Valves $
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3" 856ST
4" 856ST
6" 856ST
8" 856ST
10" 856ST
psi
22 20
18 16
14 12
10 8
6 4
2 0
psi
22 20
18 16
14 12
10 8
6 4
2 0
psi
18 16
14 12
10 8
6 4
2 0
psi
18 16
14 12
10 8
6 4
2 0
psi
18 16
14 12
10 8
6 4
2 0
psi
18 16
14 12
10 8
6 4
2 0
0 25 50 75 100 125 150 175 200 225 250 275 300 325 350 gpm 284 568 852 1136 lpm
7.5 14.7 22.0 fps
0 50 100 150 200 250 300 350 400 450 500 gpm
379 757 1136 1514 lpm
7.5 14.5 22.0 fps
0 100 200 300 400 500 600 700 800 gpm
379 1136 1893 2650 lpm
7.5 12.8 19.1 fps
0 200 400 600 800 1000 1200 1400 1600 gpm
757 2271 3785 5300 lpm
7.5 11.4 17.0 fps
0 400 800 1200 1600 2000 2400 gpm
1514 3028 4543 6057 7571 9085 lpm
7.5 10.5 15.3 fps
0 600 1200 1800 2400 3000 3600 gpm
2271 4543 6814 9085 11356 13627 lpm
7.5 9.4 14.1 fps
Service Flow
Service Flow
Service Flow
Service Flow
Service Flow
Service Flow
Rated Flow
Rated Flow
Rated Flow
Rated Flow
Rated Flow
Rated Flow
*UL Rated Flow
*UL Rated Flow
*UL Rated Flow
*UL Rated Flow
*UL Rated Flow
*UL Rated Flow
Capacity
PSI Drop
(*Friction Loss)
PSI Drop
(*Friction Loss)
PSI Drop
(*Friction Loss)
PSI Drop
(*Friction Loss)
PSI Drop
(*Friction Loss)
PSI Drop
(*Friction Loss)
ES-F-856ST 1515 © 2015 FEBCO
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A Watts Water Technologies Company
ES-F-LF866
MasterSeries® LF866
Reduced Pressure Zone
Detector Backflow Prevention
Assemblies (Type-II)
Size: 21⁄2" - 10"
LEAD FREE*
Job Name ––––––––––––––––––––––––––––––––––––––––––– Contractor –––––––––––––––––––––––––––––––––––––––––––– Job Location ––––––––––––––––––––––––––––––––––––––––– Approval ––––––––––––––––––––––––––––––––––––––––––––– Engineer ––––––––––––––––––––––––––––––––––––––––––––– Contractor’s P .O. No. ––––––––––––––––––––––––––––––––––– Approval ––––––––––––––––––––––––––––––––––––––––––––– Representative –––––––––––––––––––––––––––––––––––––––– FEBCO product specifications in U.S. customary units and metric are approximate and are provided for reference only. For precise measurements, please contact FEBCO Technical Service. FEBCO reserves the right to change or modify product design, construction, specifications, or materials with- out prior notice and without incurring any obligation to make such changes and modifications on FEBCO products previously or subsequently sold.
The FEBCO® MasterSeries® LF866 Reduced Pressure Zone
Detector Assembly is specifically designed to protect against pos- sible backpressure and backsiphonage conditions for high hazard (that is, toxic) application in accordance with Local Governing Water Utility Codes. This Backflow Assembly is primarily used on potable drinking water systems where Local Governing Codes mandate protection from non-potable quality water being pumped or siphoned back into the potable water system.
The ductile iron body is fused with ArmorTek™ coating technology to resist corrosion due to microbial induced corrosion (MIC) or exposed metal substrate. The LF866 features Lead Free construction to comply with low lead installation requirements.
The Lead Free Reduced Pressure Zone Detector Assemblies shall comply with state codes and standards, where applicable, requiring reduced lead content.
Features
Main Valve:
• Stainless steel relief valve seat and stainless steel check components for maximum performance and durability
• Inline serviceable assembly
• No special tools required for servicing
• Captured modular spring assembly
• Reversible and replaceable discs
• Field replaceable seats
• Ductile iron valve body design
• Utilizes advanced ArmorTek™ coating technology to resist corrosion of internals
• Modular and repairable pressure differential relief valve • Clapper check assembly
• Captured O-ring design
Auxiliary Bypass:
• Compact bypass design; remains in main valve assembly profile • Inline serviceable
3⁄4" check assembly
• No special tools required for servicing
• Field replaceable seat and disc
• Detect potential underground water leaks
• Detect unauthorized water usage
Specification
The FEBCO MasterSeries LF866 Reduced Pressure Zone
Detector Assembly shall be installed on the potable water supply and at each point of cross-connection to protect against possible backpressure high hazard and backsiphonage conditions for (that is, toxic) applications. The assembly shall consist of a main line valve body composed of two (2) independently acting approved clapper style check modules with replaceable seats and disc rub- bers. Servicing of both check modules does not require any spe- cial tools and are accessed through independent top entry covers.
This assembly shall be fitted with approved UL/FM inlet/outlet resilient seated shutoff valves and contain four (4) properly located resilient seated test cocks as specified by AWWA Standard C511. The auxiliary bypass line contains a
5⁄8"x 3⁄4" Water Meter
that complies with ANSI/AWWA Standard C700 coupled with an approved check assembly compliant to AWWA Standard C511.
The bypass line is designed to detect leaks or unauthorized water usage of the water system while protecting against possible backpressure and backsiphonage conditions in high hazard (i.e., toxic) applications. The valve body shall utilize a coating system with built-in electrochemical corrosion inhibitor and microbial inhibitor. Flow and pressure loss performance parameters shall meet the requirements of AWWA Standard C511.
NOTICE
Inquire with governing authorities for local installation requirements.
Model LF866-OSY
NOTICE
The information contained herein is not intended to replace the full product installation and safety information available or the experience of a trained product installer. You are required to thoroughly read all installation instructions and product safety information before beginning the installation of this product.
Engineering Specification
*The wetted surface of this product contacted by consumable water contains less than 0.25% of lead by weight.
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Options - Suffix
OSY: UL/FM Approved OS&Y gate valves
(ANSI/AWWA C515 Compliant)
CFM: Totalizing cubic ft/min 5⁄8" x ¾" water meter
(ANSI/AWWA C700 Compliant)
GPM: Totalizing gal/min 5⁄8"x ¾" water meter
(ANSI/AWWA C700 Compliant)
LG: Less shutoff valves (This is NOT an APPROVED ASSEMBLY.) Example Ordering Descriptions
4" LF866V-OSY-GPM - Assembly fitted with OS&Y shutoff valves and gallons per minute water meter
4" LF866V-OSY-CFM - Assembly fitted with OS&Y shutoff valves and cubic feet per minute water meter
Assembly Flow Orientation
Horizontal (21⁄2" – 10") - Approved by FCCCHR-USC, ASSE, cULus,
FM, IAPMO
Materials
All sizes (2½" – 10") are similar in materials and construction.
Contact your local FEBCO representative if you require further information.
Main Valve Body: Ductile iron Grade 65-45-12
Relief Valve Body: Ductile iron Grade 65-45-12
Coating: Fusion epoxy coated internal and external
AWWA C550-90
Shutoff Valves: OSY resilient wedge gate valve AWWA C515 (UL/FM)
Check Seats: Stainless steel
Relief Valve Seat: Stainless steel
Disc Holder: Stainless steel
Elastomer Disc: Silicone
Spring: Stainless steel
Clamp: AWWA C606 (10" only)
Approvals – Standards
• Foundation for Cross-Connection Control and Hydraulic Research at The University of Southern California
(FCCCHR-USC)
• ASSE 1047
• UL Classified** (US & Canada)
• FM Approved**
• IAPMO/cUPC
**Assembly configured with UL/FM Approved OS&Y RWgate
valves. Less gate valve assemblies are not UL/FM approved configurations.
Standards
• AWWA Standard C511 Compliant
• End Connections: Compliant to ASME B16.1 Class 125 & AWWA Class D Flange
Pressure - Temperature
Max. Working Pressure: 175 psi (12.1 bar)
Min. Working Pressure: 20 psi (1.4 bar)
Hydrostatic Test Pressure: 350 psi (24.1 bar)
Hydrostatic Safety Pressure: 700 psi (48.3 bar)
Temperature Range: 33°F – 140°F (0.5°C – 60°C)
continuous
1047
** **
Shutoff
Valve #1
Test Cock
#3
First Spring
Assembly
Second Spring
Assembly
Second Check
Assembly
First Check
Assembly
Test Cock
#1 Test Cock
#2
Relief Valve
Assembly
Test Cock
#4
Shutoff
Valve #2
MODEL LF866 ASSEMBLIES
SIZE DIMENSIONS WEIGHT**
A B C D E* F G H OSY
in. in. mm in. mm in. mm in mm in. mm in. mm in. mm in. mm lb kg 21⁄2 403⁄4 1035 25 1⁄2 648 12 1⁄8 308 10 254 16 3⁄8 416 4 1⁄2 114 7 1⁄8 181 5 7⁄8 150 218 99 34 1 7⁄8 1064 25 5⁄8 651 12 1⁄8 308 10 254 22 1⁄8 565 4 1⁄2 114 7 3⁄8 187 6 1⁄4 159 245 111 44 6 1⁄4 1175 28 711 12 1⁄2 318 10 1⁄8 257 23 1⁄4 591 5 1⁄2 140 8 1⁄8 206 7 178 324 147 6 56 1422 34 3⁄4 883 15 384 11 1⁄8 283 30 1⁄8 765 6 1⁄2 165 9 7⁄8 251 9 229 520 236 8 65 1651 41 3⁄4 1061 17 1⁄8 434 12 1⁄4 311 37 3⁄4 959 7 178 11 1⁄8 283 9 1⁄2 241 835 379 10 72 5⁄8 1845 46 3⁄8 1178 17 1⁄8 434 12 3⁄8 314 48 1219 9 229 12 3⁄8 314 10 1⁄2 267 1240 562 Note:
* Indicates nominal dimensions with OSY gate valves (full open position) ** Indicates weight of complete backflow assemblies with specified gate valves The gap drain is not designed to catch the maximum discharge possible from the relief valve. The installation of the FEBCO air gap with the drain line terminating above a floor drain will handle any normal discharge or nuisance spitting through the relief valve. However, floor drain size may need to be designed to prevent water damage caused by a catastrophic failure condition. Do not reduce the size of the drain line from the air gap fitting. $
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Dimensions & Weights
Below are the nominal dimensions and physical weights for Series LF866, sizes 2½" to 10". Allowances must be made for normal manufacturing tolerances. Download installation instructions at watts.com, or contact your local FEBCO representative for more information.
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Performance
The flow capacity chart identifies valve performance based upon rated water velocity up to 20fps.
• Maximum service flow rate is determined by maximum rated velocity of 7.5fps.
• AWWA Manual M-22 (Appendix C) recommends that the maximum water velocity in the services be not more than 10fps.
• UL flow rate is determined by typically rated velocity of 15 ft/sec.
USA: T: (800) 767-1234 • F: (800) 788-4491 • FEBCOonline.com Canada: T: (888) 208-8927 • F: (905) 481-2316 • FEBCOonline.ca Latin America: T: (52) 55-4122-0138 • FEBCOonline.com
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SSEWER AREA STUDY
VTTM 84968
Prepared for
MW Investment Group, LLC
27702 Crown Valley Parkway, Ste. D-4-197
Ladera Ranch, CA 92694
Contact: MaƩ Waken
Property:
201 Colorado Place
Arcadia, CA 91007
APN: 5775-011-032 & 5775-011-031
Prepared by:
C&V ConsulƟng, Inc.
9830 Irvine Center Dr.
Irvine, CA 92630
Contact: Antonio Ruiz
(949) 445 - 1771
Dane P . McDougall R.C.E. 80705
Prepared: January 2026
1/27/2026
Table of Contents
SECTION PAGE
INTRODUCTION 1
SITE DESCRIPTION 1
PROJECT DESCRIPTION 2
METHODOLOGY 3 - 4 SEWER PIPE CAPACITY ANALYSIS 5 - 6
CONCLUSION 7
Appendices
A. SEWER AREA STUDY EXHIBIT
B. SEWER AREA STUDY TABLE & DEPTH OF FLOW CALCULATIONS
C. SEWER ATLAS MAP & SEWER AS-BUILTS
D. VESTING TENATIVE TRACT MAP (VTTM)
E. COUNTY OF LOS ANGELES DEPARTMENT OF PUBLIC WORKS, SEWER DESIGN GUIDELINES F. LOS ANGELES COUNTY SANITATION DISTRICT – WILL SERVE LETTER G. CITY OF ARCADIA ZONING MAP
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Sewer Area Study
Arcadia, VTTM 84968
2 PROJECT DESCRIPTION
The site is approximately 3.7 gross acres as measured to the exisƟng right-of-way. The proposed development will consist of eighty-six (86) townhome units, with primary access to the project provided by Colorado Place. The site will include private driving aisles, hardscape, parking areas, associated landscaping and the proposed sewer system will be gravity fed.
AP Number Size (ac)
5775-011-032 1.3
5775-011-032 2.4
Total Site 3.7
Sewer Area Study
Arcadia, VTTM 84968
3 METHODOLOGY
This study will inves Ɵgate the sewerage discharge route from the proposed development to the exis Ɵng SanitaƟon District No. 15 Santa Anita Ou ƞall 21” trunk sewer main, located on W . HunƟngton Drive. The subject route of the sewer main will be analyzed by segments based on sewer pipe size, slope and tributary area.
Reach #1.1 segment is on Colorado Place, from Arcadia city manhole 507_MH 008 to 507_MH 082 and consists of an exisƟng 10” VCP sewer main with a slope of 1.12%. This segment includes the northern sec Ɵon of the project site (Area S), and the upstream tributary areas 1A, 1B and 1C.
Reach #1.2 segment is on Colorado Place, from Arcadia city manhole 507_MH 082 to 508_MH 001 and consists of an exisƟng 10” VCP sewer main with a slope of 1.12%. This segment includes the southern sec Ɵon of the project site (Area S), and the upstream tributary areas.
Reach #2 segment is on Colorado Place, from Arcadia city manhole 508_MH 001 to 508_MH 002 and consists of an exisƟng 10” VCP sewer main with a slope of 0.92%. This segment includes areas 2A, 2B, and 2C, in addiƟon to all the upstream tributary areas.
Reach #3 segment is on Colorado Place, from Arcadia city manhole 508_MH 002 to 508_MH 003 and consists of an exisƟng 12” VCP sewer main with a slope of 0.56%. This segment includes area and all upstream tributary areas.
Reach #4 segment is on Colorado Place, from Arcadia city manhole 508_MH 003 to 508_MH 004 and consists of an exisƟng 12” VCP sewer main with a slope of 0.54%. This segment includes area 4 and all the upstream tributary areas.
Reach #5 segment is on Colorado Place and Hun Ɵngton Drive, from Arcadia ci ty manhole 508_MH 004 to 508_MH 012 and consists of an exisƟng 12” VCP sewer main with a slope of 0.56%. This segment includes area 5 and all the upstream tributary areas.
Reach #6 segment is on HunƟngton Drive, from Arcadia city manhole 508_MH 012 to 508_MH 013 and consists of an exisƟng 14” HDPE sewer main with a slope of 1.32 %. Th is segment includes area 6A, 6B, 6C, and 6D in addi Ɵon to all the upstream tributary areas.
Reach # 7 segment is on HunƟngton Drive, from Arcadia city manhole 508_MH 013 to 508_MH 014 and consists of an exisƟng 14” HDPE sewer main wit a slope of 1.10 %. This segment includes area 7 in addi Ɵon to all the upstream tributary areas of reach #6.
Sewer Area Study
Arcadia, VTTM 84968
4 Reach #8 segment is on HunƟngton Drive, from Arcadia city manhole 508_MH 014 to 508_MH 015 and consists of an exisƟng 14” HDPE sewer main with a slope of 1.10 %. This segment contributes no addi Ɵonal flow but includes all the upstream tributary areas.
Reach #9 segment is on HunƟngton Drive, from Arcadia city manhole 508_MH 015 to 508_MH 016 and consists of a 2 x 10” siphon with an assumed slope of 1.10 %. This segment contributes no addi Ɵonal flow and due to siphons hydraulic behavior differing from the surrounding gravity led mains it has been excluded from the calculaƟons.
Reach #10 segment is on HunƟngton Drive, from Arcadia city manhole 508_MH 016 to 408_MH 004 and consists of an exisƟng 14” HDPE sewer main with a slope of 1.20 %. This segment contributes no addi Ɵonal flow but includes all the upstream tributary areas.
Reach #11 segment is on HunƟngton Drive, from Arcadia city manhole 408_MH 004 to 408_MH 002 and consists of an exisƟng 14” HDPE sewer main with a slope of 1.20 %. This segment includes areas 11A and 11B in and includes all the upstream tributary areas.
Reach #12 segment is on HunƟngton Drive, from Arcadia city manhole 408_MH 002 to 409_MH 004 and consists of an exisƟng 14” HDPE sewer main with a slope of 1.20 %. This segment includes area 12 in addiƟon to all the upstream tributary areas.
Reach #13 segment is on HunƟngton Drive, from Arcadia city manhole 409_MH 004 to 409_MH 006 and consists of an exisƟng 16” HDPE sewer main with a slope of 0.50 %. This segment contributes no addi Ɵonal flow but includes all upstream tributary areas.
Reach #14 segment is on HunƟngton Drive, from Arcadia city manhole 409_MH 006 to 409_MH 007 and consists of an exisƟng 2 x 12” V.C.P siphon. This segment contributes no addi Ɵonal flow and due to siphons hydraulic behavior differing from the surrounding gravity led mains it has been excluded from the calculaƟons.
Reach #15 segment is on HunƟngton Drive, from Arcadia city manhole 409_MH 007 to 409_MH 003 which serves as the point of connec Ɵon to the 21” Santa Anita Ou ƞall Trunk, this segment consists of an exis Ɵng 16” HDPE with a slope of 0.20 %. This segment contributes no addiƟonal flow but includes all upstream tributary areas.
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Sewer Area Study
Arcadia, VTTM 84968
6 The downstream tributary areas were calculated by reference scaling City of Arcadia Sewer Atlas Maps and referencing County of Los Angele s Assessor’s map. The zoning coe fficients were referencing the LACDPW guidelines and the Zoning Map provided by the City of Arcadia in Appendix G. *Reach #9 and #14 consist of siphons and have been excluded from the calculaƟons due to Mannings equaƟon not being applicable to these segments.*
City of Arcadia’s classificaƟon of R-1 and R-3 matches the density descrip Ɵons of Los Angeles County Zones R-1 and R-3, so the LACPWD zoning coefficients were applied respecƟvely.
City of Arcadia’s commercial classificaƟons of C-G falls under the commercial LACPWD zoning, so the commercial coefficient was applied to all C-G parcels in the tributary area.
Hotels, hospitals, medical buildings, condominiums, and office buildings were taken into consideraƟon of separate calculaƟons. Per County requirements, sewage flow from the above-menƟoned areas are calculated based on the formulas below.
Area Formula
Hotels (150 gals)/(# of rooms)
Hospitals (Surgical) (500 gals)/(# of beds)
Medical buildings (300 gals)/(1000 sq Ō gross floor area) Condominiums 0.001 (cfs/unit)
Office buildings (200 gals)/(1000 sq Ō gross floor area)
(Refer to the LACDPW guideline informaƟon within Appendix E)
Sewer Area Study
Arcadia, VTTM 84968
7 CONCLUSION
The exis Ɵng sewer system being analyzed in this area study has a design capacity above the calculated cumula Ɵve flow. The peak discharge at the downstream end of the sewer system entering the 21” SanitaƟon District No. 15 Santa Anita Ouƞall Trunk Sewer is calculated to be a rate of 2.4840 cfs represenƟng approximately 80% cumulaƟve flow capacity. Reach #2 has the highest cumulaƟve flow percentage of approximately 96%. Therefore, we conclude that the exisƟng sewer system has adequate capacity for the proposed development.
Further confirmaƟon of the exisƟng sewer system’s ability to support the development has been verified by the city of Arcadia. Flow monito ring was conducted at manhole 507_MH_082 and confirmed that the peak flow depth of the exis Ɵng 10” V.C.P . on Colorado Place just upstream of reach #1 is 3.94 inches corresponding to a d/D of 0.394. Using a Mannings n value of 0.013 that would correspond to a flow rate of 0.760 cfs represen Ɵng approximately 70% capacity of the exisƟng sewer system. AddiƟonally, the city of Arcadia has esƟmated that the peak flow from San Juan drive was esƟmated to be approximately 0.08 cfs. The proposed development is esƟmated to add approximately 0.0975 cfs of e ffluent which would put the 10” V.C.P . on Colorado Place corresponding to reach #1.2 at approximately 73% capacity.
Refer to Appendix B for calculaƟons and tabulated results.
Sewer Area Study
Arcadia, VTTM 84968
8 Appendix A
SEWER AREA STUDY EXHIBIT
1" = 305'
S
2A2A
2B
1A
1B
1C
2C
3 4 5 6A
6B
6B6B
6B
6B
6B
6B
6B
6B
6B
6B
6B
6B
6C
6D
11A11B
12 7
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C 1C 1C
1C
1C
1C
1C
1C
1C
2B
2B
2B
1C
1C1C
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C
1C1C
1C
1C
1C
1C
Sewer Area Study
Arcadia, VTTM 84968
9 Appendix B
SEWER AREA STUDY TABLE & DEPTH OF
FLOW CALCUATIONS
TR 949
201 Colorado Place, Arcadia
Percentage Full
MH # MH # Size
(in.)
Slope
(%) 1/2 Full 3/4 Full Cumulative Flow/
Capacity
507_8 507_82 10 1.12 1.088 S(Site N) Proposed Townhomes (2 Bedroom) 0.0039 (4 units) (250
gal/day)*2.5 = 2500
gal/day = 0.0039 cfs
S(Site N) Proposed Townhomes (3+ Bedroom) 0.0615
(53 units)(300
gal/day)* 2.5 = 39750
gal/day = 0.0615 cfs
1A 7.96 C-G - General Commercial Flow monitoring data
used
1C 519.10 R-1 - Low Density Residential Flow monitoring data used
1B 1.29 R-3 - High Density Residential 0.7600 Flow monitoring data used 70%
Reach #1.2
507_83 508_1 10 0.12 1.088 S(Site S) Proposed Townhomes (2 Bedroom) 0.0077 (8 units) (250
gal/day)*2.5 = 2500
gal/day = 0.0077 cfs
Colorado Place Site S Proposed Townhomes (3+ Bedroom) 0.0244 0.7921 (21 units)(300
gal/day)* 2.5 = 39750
gal/day = 0.0244 cfs
73%
508_1 508_2 10 0.92 0.986 2A 1.73 R-3 - High Density Residential 0.08 cfs from San Juan
2B 103.49 R-1 - Low Density Residential 0.08 cfs from San Juan
2C 0.61 Prop. Hotel (Guest Rooms) 0.0528
(91 rooms)(150
gal/day)*2.5 =34125
gal/day = 0.0528 cfs
Prop. Hotel (Employee Break Room) 0.0013
(1633/1000 sqft)(200
gal/day) *2.5 = 817
gal/day = 0.0013 cfs
Prop. Hotel (Laundry Room &
Fitness) 0.0012
(2 room * 150 gal/day)
*2.5 =750 gal/day =
0.0012 cfs
Prop. Hotel (Bar) 0.0019
(25 occupants) (20
gal/day) *2.5 = 1250
gal/day = 0.0019 cfs
Prop. Hotel (Café) 0.0135 0.9428
(70 occupants)(50
gal/day) *2.5 = 8750
gal/day = 0.0135
96%
Comments
Reach #1.1
Colorado Place Site N
Sewer Area Study Table - With Proposed Project
Street Name
Segment Pipe *Capacity (cfs) Calculated
Peak Flow
(cfs)
**Cumulative
Calculated Peak
Flow (cfs)
Tributary Area (Acres) Zone (LA County Factor) Zoning
Coefficient
Tributary
Area #
Reach #2
Colorado Place Segment A
1/30/2026
CVC Job No MWIG-010 1
508_2 508_3 12 0.56 1.272 3 Keck Medical Building (A) 0.0230 (19,845/1000 sqft)(300
gal/day)*2.5 = 14,884 =
0.6880 cfs
Keck Medical Building (B) 0.0223 0.9881 (19,231/1000 sqft)(300 gal/day)*2.5 = 14,423 = 78%
508_3 508_4 12 0.54 1.249 4 Prop. Hotel Building C (Guest Rooms) 0.0522
(90 rooms)(150
gal/day)*2.5 = 33750
gal/day = 0.0522 cfs
Reach #4
Colorado Place Segment C Prop. Hotel Building C (Resturant) 0.0534 (276 occupants)(50
gal/day)*2.5 = 34,500
gal/day = 0.0534 cfs
Prop. Hotel Building C (Bar) 0.0053 1.0991
(69 occupants)(20
gal/day)*2.5 = 3,443
gal/day = 0.0053 cfs
88%
508_4 508_12 12 0.56 1.272 5 Prop. Hotel Building D (Guest Rooms) 0.0435
(75 rooms)(150
gal/day)*2.5 =28,125
gal/day = 0.435 cfs
Prop. Hotel (Cafe) 0.0203
(105 occupants)(50
gal/day)*2.5 = 13,125
gal/day = 0.0203
Prop. Hotel (Spa) 0.0188 1.1817
(7466/1000 sqft) (650
gal/day) * 2.5 = 12,132
gal/day = 0.0188 cfs
93%
508_12 508_13 14 1.32 5.539 6A 1.37 C-G - General Commercial 0.015 0.0205 6B 48.99 R-1 - Low Density Residential 0.004 0.1960
6C 2.75 Park 0.001 0.0028
6D 2.75 Hotel (Guest Rooms) 0.1352
(233 rooms) (150
gal/day) * 2.5 = 87375
gal/day = 0.1352 cfs
Hotel (Conference Rooms) 0.0034
(7324/1000 sqft) (120
gal/day)*2.5 = 2197
gal/day = 0.0034 cfs
Hotel (Laundry Room & Fitness) 0.0012
(2 room * 150 gal/day)
*2.5 =750 gal/day =
0.0012 cfs
Hotel (Resturant) 0.0716 1.6122
(370 occupants)(50
gal/day) *2.5 = 46250 =
0.0176 cfs
29%
Reach #5
Colorado Place & Huntington Dr.
Reach #6
Huntington Dr. Segment A
Reach #3
Colorado Place Segment B
1/30/2026
CVC Job No MWIG-010 2
508_13 508_14 14 1.10 5.055 7 2.95 Prop. Mixed Use (Retail/Commercial) 0.007397 (19123/1000 sqft)(100
gal/day)*2.5 = 4781 =
0.007397 cfs
Prop. Mixed Use (Office) 0.009599
(12408/1000 sqft)(200
gal/day) *2.5 = 6204
gal/day = 0.009599 cfs
Prop. Mixed Use (Spa) 0.0168
(6665/1000 sqft)(650
gal/day) * 2.5 = 10831
gal/day = 0.0168 cfs
Prop. Mixed Use (Condominums) 0.0960 1.7420 (96 units)(0.001 cfs) =
0.096 cfs 34%
508_14 508_15 14 1.10 5.055 0.0000 1.7420 No additional flow 34%
1.7420 Siphon excluded from
calculations
508_16 408_4 14 0.12 5.281 0.0000 1.7420 No additional flow 33% 408_4 408_2 14 0.12 5.281 11A 7.73 Recreational 0.001 0.0077 Reach #11
Huntington Dr. & Centennial N 11B 5.71 Office Building 0.0612 1.8109 (79172/1000 sqft)(200
gal/day)*2.5 = 39586
gal/day = 0.0612 cfs
34%
408_2 409_4 14 0.12 5.281 12 16.18 USC Arcadia Hospital 0.6730 2.4840 (348 beds)(500
gal/day)*2.5 = 435000
gal/day = 0.6730 cfs
47%
409_4 409_6 16 0.500 4.902 0.0000 2.4840 No additional flow 51% Reach #13
Huntington Dr. Segment E
Reach #10
Huntington Dr. Segment D
Reach #12
Huntington Dr. & Centennial S
Reach #9
Huntington Dr. Siphon A
Reach #8
Huntington Dr. Segment C
Reach #7
Huntington Dr. Segment B
1/30/2026
CVC Job No MWIG-010 3
2.4840 Siphon excluded from
calculations
409_7 409_3 16 0.200 3.086 0.0000 2.4840 No additional flow 80% Reach #15
Huntington Dr. POC
Reach #14
Huntington Dr. Siphon B
1/30/2026
CVC Job No MWIG-010 4
Pipe Diameter 10 in
Pipe Diameter 0.833 ft
Depth of Flow (50% full) 0.417 ft
Slope 0.0112 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 3.142 radians
Flow Area 0.273 sf
Wetted Perimeter 1.309 ft
Hydraulic Radius 0.208 ft
Pipe Capacity 1.088 cfs
Kutter's Formula
Reach 1.1 &1.2 Pipe Capacity
Pipe Diameter 10 in
Pipe Diameter 0.833 ft
Depth of Flow (50% full) 0.417 ft
Slope 0.0092 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 3.142 radians
Flow Area 0.273 sf
Wetted Perimeter 1.309 ft
Hydraulic Radius 0.208 ft
Pipe Capacity 0.986 cfs
Kutter's Formula
Reach 2 Pipe Capacity
Pipe Diameter 12 in
Pipe Diameter 1.000 ft
Depth of Flow (50% full) 0.500 ft
Slope 0.0056 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 3.142 radians
Flow Area 0.393 sf
Wetted Perimeter 1.571 ft
Hydraulic Radius 0.250 ft
Pipe Capacity 1.272 cfs
Kutter's Formula
Reach 3 & 5 Pipe Capacity
Pipe Diameter 12 in
Pipe Diameter 1.000 ft
Depth of Flow (50% full) 0.500 ft
Slope 0.0054 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 3.142 radians
Flow Area 0.393 sf
Wetted Perimeter 1.571 ft
Hydraulic Radius 0.250 ft
Pipe Capacity 1.249 cfs
Kutter's Formula
Reach 4 Pipe Capacity
Pipe Diameter 14 in
Pipe Diameter 1.167 ft
Depth of Flow (75% full) 0.875 ft
Slope 0.0132 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 2.094 radians
Flow Area 0.860 sf
Wetted Perimeter 2.443 ft
Hydraulic Radius 0.352 ft
Pipe Capacity 5.539 cfs
Kutter's Formula
Reach 6 Pipe Capacity
Pipe Diameter 14 in
Pipe Diameter 1.167 ft
Depth of Flow (75% full) 0.875 ft
Slope 0.0110 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 2.094 radians
Flow Area 0.860 sf
Wetted Perimeter 2.443 ft
Hydraulic Radius 0.352 ft
Pipe Capacity 5.055 cfs
Kutter's Formula
Reach 7 & 8 Pipe Capacity
Pipe Diameter 12 in
Pipe Diameter 1.000 ft
Depth of Flow (75% full) 0.750 ft
Slope 0.0120 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 2.094 radians
Flow Area 0.632 sf
Wetted Perimeter 2.094 ft
Hydraulic Radius 0.302 ft
Pipe Capacity 3.459 cfs
Kutter's Formula
Reach 10-12 Pipe Capacity
Pipe Diameter 16 in
Pipe Diameter 1.333 ft
Depth of Flow (75% full) 1.000 ft
Slope 0.0050 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 2.094 radians
Flow Area 1.123 sf
Wetted Perimeter 2.793 ft
Hydraulic Radius 0.402 ft
Pipe Capacity 4.902 cfs
Kutter's Formula
Reach 13 Pipe Capacity
Pipe Diameter 16 in
Pipe Diameter 1.333 ft
Depth of Flow (75% full) 1.000 ft
Slope 0.0020 ft/ft
Manning's Roughness
Coefficient (n) 0.013 (unitless)
Central Angle 2.094 radians
Flow Area 1.123 sf
Wetted Perimeter 2.793 ft
Hydraulic Radius 0.402 ft
Pipe Capacity 3.086 cfs
Reach 15 Pipe Capacity
Kutter's Formula
Sewer Area Study
Arcadia, VTTM 84968
10 Appendix C
SEWER AS-BUILTS & ATLAS MAPS
508_MH 001
507_MH 015
507_MH 015
507_MH 014
508_MH 012
508_MH 003 508_MH 004
508_MH 002
508_MH 001
507_MH 008
507_MH 082
POC N
Project Site
2x10" VCP Siphon
507_MH 082
507_MH 083
POC S
508_MH 004
409MH025
DISCLAIMER: THE COUNTY SANITATION DISTRICTS OF LOS ANGELES COUNTY (DISTRICTS) PROVIDE THIS INFORMATION “AS IS” FOR GENERAL REFERENCE ONLY. THE DISTRICTS DO NOT GUARANTEE OR WARRANT THE ACCURACY OF ANY INFORMATION SHOWN OR THE DRAWINGS AVAILABLE FOR DOWNLOAD. THE DISTRICTS DISCLAIM ANY EXPRESS OR IMPLIED WARRANTY. THIS INFORMATION SHOULD NOT BE RELIED UPON FOR CONSTRUCTION. THE INFORMATION MAY REFLECT ONLY AS-PLANNED LOCATIONS AND DOES NOT NECESSARILY ACCURATELY REFLECT THE LOCATIONS OF AS-BUILT FACILITIES OR SUBSEQUENTLY BUILT FACILITIES. APPROPRIATE FIELD VERIFICATION IS REQUIRED IN ORDER TO DETERMINE THE EXACT LOCATION OF DISTRICTS' FACILITIES. FACILITIES WITHIN DISTRICTS' PROPERTY ARE NOT SHOWN. ANY PERSON PERFORMING EXCAVATION MUST COMPLY WITH CALIFORNIA GOVERNMENT CODE SECTION 4216.
NOTE THAT "SUBSURFACE INSTALLATIONS" AS DEFINED BY CALIFORNIA GOVERNMENT CODE SECTION 4216 EXCLUDES NON-PRESSURIZED SEWERS, NON-PRESSURIZED STORM DRAINS, AND OTHER NON-PRESSURIZED DRAIN LINES. ANY PERSON PLANNING TO CONSTRUCT IMPROVEMENTS OVER OR BELOW DISTRICTS' FACILITIES WITHIN PRIVATE RIGHT-OF-WAY SHALL OBTAIN A BUILDOVER AGREEMENT PRIOR TO CONSTRUCTION.
LACSD POC.
MH - 15 0580
4.0 3.0
5.0 8.0
28.7 287.5
300.5
6.0 15.0
17.0 4.5'
4.0 3.0
8'' VCP
12.04%
8'' V
CP
12.0 0%
8'' VCP
9.40%
8'' VCP8.24%
8''
VCP
5.84%
8'' VCP
11.64%
8'' VCP
7.48%
8'' VCP
10.16%
8'' VCP13.76% 8'' VC
P
11.72%
8'' VCP
10.88%
8''
VCP
12.08%
8'' VCP
12.60%8'' VCP
11.08%
0.88%8'' VCP
0.40%
8'' VCP5.72%
4.12%
8'' VCP
8'' VCP
11.96%
8'' VCP
8.438%
8'' VCP10
.12%
8'' VCP
11.32%
8'' VCP
18%
8'' VCP
8'' VCP 8'' VCP
8'' V
CP
0%
8'' VC
P
2.2 %
8'' VCP
2.84%
3.96%
8'' VC
P
13%
8'' V
CP
12.20%
8'' VCP
4.52%
3.76%
8''
VCP9.
58%
8'' VCP15.20%
8''
VCP
11.72%
8'' VCP
10.40%
8'' VCP10.16%8'' VCP
6.22%
8'' VCP
6.64%
8'' VCP
3.608%
8'' VCP9.24%
8'' VCP7.76%
8'' VCP
6.52%
8'' VCP
3.92%
8'' VC
P
5.593%
8'' VC
P
3.60%
8'' VCP7.12%
8'' VCP11.20%
8'' VCP4.48%
8'' VCP
2.48%
8'' VCP
11.00%
8'' VCP
14 .32%
8'' VCP
9.64%
8'' VC
P
10.16%
8'' VC
P 2.60%
8'' VCP
3.36%
8'' VCP
0.68 %8'' VCP
0.40 %
8'' VCP
2.60%
8'' V
CP8.20%
8'' VC
P
0.48%
8'' VCP0.40%
8'' VCP3.28%
7.75%
8'' VCP
7.18%
8'' VCP
1.70%
8'' VCP
1.20%
8'' VCP
1.40%
8'' VCP
1.30%
8'' VCP
1.20%
8'' VCP 8'' VCP 8'' VCP
8'' VCP 8'' VCP 8'' VCP
8'' VCP
8'' VCP 8'' VCP
8'' VCP
8'' VCP
0.40%
8'' VCP
3.622%
8'' VCP 8'' VCP
8'' VCP8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
1.17%
8'' VCP
1.00%
8'' VCP
0.56%
8'' VCP 8'' VCP 8'' VCP
8'' VCP
8'' VCP
0.50%
8'' VCP
0.5%
8'' VCP
0.50%
8'' VCP
8'' VCP 8'' VCP
8'' VCP 8'' VCP 8'' VCP8'' VCP
0.32%
8'' VCP
0.4%
8'' VCP
8'' VCP
1.20%
8'' VCP
1.17%
8'' VCP
0.70%
8'' VCP
0.40%
8'' VCP
1.18%
8'' VCP
1.18%
10'' VCP
0.32%
10'' VCP
0.16%
10'' VCP
0.16%
8'' VCP
1.17%
8'' VCP
1.20%
8'' VCP
1.17%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.44%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
1.17%
8'' VCP
1.40%
8'' VCP
0.80%
8'' VCP
0.40%
8'' VCP
1.20%
8'' VCP
0.32%
8'' VCP
1.00%
10'' VCP0.32%
0.95%
10'' VCP
0.95%
8'' VCP
1.60%
8'' VCP
1.60%
10'' VCP
0.95%
8'' VCP 1.28%
8'' VCP
1.00%
10'' VCP
0.95%
8'' VCP
1.00%
10'' VCP
1.29%
8'' VCP
8'' VCP
0.40%
8'' VCP
1.50%
8'' VCP
0.40%
8'' VCP
0.40%
8'' VCP
1.32%8'' VCP
1.60%
8'' VCP 0.40%
8'' VCP
0.40%
8'' VCP
0.40%
8'' VCP
1.20%
8'' VCP
2.00%
8'' VCP
1.30%
14'' HDPE1.10%
2 x 10'' VCP SIPHON
14'' HDPE1.20%
10'' VCP
0.92%
12'' VCP
0.56%
8'' VCP
0.50%
12''
VCP
12'' VCP
14'' HDPE
1.32%
14'' HDPE
1.10%
8'' VCP0.80%
8'' VCP
1.40%
8'' VCP
0.50%
8'' VCP
0.70%
8'' VCP
0.50%
8'' VCP
0.50%
8'' VCP
1.20%
8'' VCP
1.50%
8'' VCP
0.30%
8'' VCP
1.00%
8'' VCP1.50%
8'' VCP
0.30%
8'' VCP
1.20%
8'' VCP
0.30%
8'' VCP
0.40%
8'' VCP
0.40%
8'' VCP
0.50%
8'' VCP
1.30%
8'' VCP
8'' VCP
1.00%
8'' VCP
0.50%
8'' VCP
0.50%
8'' VCP
0.32%
8'' VCP8'' VCP
8'' VCP
1.50%
8'' VCP
1.60%
8'' VCP0.92%
8'' VCP0.92%
8'' VCP
0%
8'' VCP
1.904%
8'' VCP
0%
8'' VCP
0%
8'' VCP
0.4%8'' VCP
1.00%
8'' VCP
1.50%
8'' VCP
0.40%
8'' VCP
0.50%
8'' VCP
1.5%
8'' VCP
0.40%
8'' VCP
8'' VCP
1.12%
10'' VCP
10'' VCP1.85%
8'' VCP 8'' VCP
1.60%
8'' VCP
1.30%
8'' VCP
1.60%
10' VCP
1.58%
8'' VCP
8'' VCP
8'' VCP
2 x 10'' VCP SIPHON
8'' VCP
8'' VCP
8'' VCP
8'' VCP8'' VCP
8'' VCP
8'' VCP
1.40%
8'' VCP
8''
VCP
8'' VCP
8'' VCP
8'' VCP1.40%
8'' VCP
0%
8'' VCP
8'' VCP
10'
' VCP
1.12%
8'' VCP1.8%
8'' VCP
8'' VCP
1.3%
8'' VCP
1.50%8'' VCP
1.00%
8'' VCP
0.40%
8'' VCP
0.40%
15'' VCP 0.75%15'' VCP 0.75%
8'' VCP0%
15'' VCP RELIEF SEWER
8'' VCP
0%
15'' VCP
0.75%
8'' VCP 0%
8'' VCP
0.40%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.50%
8'' VCP
0.50%
8'' VCP
0.32%
8'' VCP 0%
8'' VCP
1.28%
8'' VCP
1.30%
8'' VCP
0.64%
8'' VCP
0%
8'' VCP
1.30%8'' VCP
1.24%
10'' VCP
0.64%
8'' VCP
0.44%
10'' VCP
0.64%
8'' VCP
1.24%
8'' VCP
1.00%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.32%
8'' VCP
0.40%
8'' VCP
0.40%
10'' VCP
1.08%
10'' VCP
1.28%
8'' VCP 0.64%
8'' VCP
0.40%
10'' VCP
1.28%
10'' VCP
1.28%
8'' VCP
1.10%
8'' VCP
0.4%
10'' VCP
8'' VCP 0.40%
8'' VCP
0.4%
8'' VCP
0.4%
8'' VCP
0.40%
8'' VCP
0.40%
8'' VCP
1.00%
8'' VCP
0.40%
8'' VCP
0.50%
8'' VCP
0.40%
8'' VCP
0.40%
10'' VCP
1.08%
8'' VCP
1.00%
8'' VCP
1.20%
15'' VCP
0%
15'' VCP 0.75%
8'' VCP
0.50%
8'' VCP
0.50%
8'' VCP
0.50%
8'' VCP
0.50%
8'' VCP
5.50%
8'' VCP
0.47%
8'' VCP
0.47%
8'' VCP
0.47%
8'' VCP
1.00%
8'' VCP
0.40%
8'' VCP
0.40%
8'' VCP
0.4%
8'' VCP
0.64%
8'' VCP
0.64%
8'' VCP
1.41%
15'' VCP
0%
15'' VCP
12'' VCP SIPHON
8'' VCP
0.4%
8'' VCP1.56%
8'' VCP
1.00%
8'' VCP
1.00%
8'' VCP
1.28%
8'' VCP
1.28%
24'' VCP
0%
8'' VCP
0.44%
24'' VCP
0%
24'' VCP
0% 8'' VCP0.4%
8'' VCP1.60%
8'' VCP1.30%
8'' VCP
3.72%
8'' VCP
1.36%8'' VCP
0.24%
8'' VCP
0.40%
8'' VCP
1.36%
8'' VCP
0.68%
8'' VCP0.40%
8'' VCP2.20%
8'' VCP2.40%
8'' VCP
0%
24'' VCP
0%
8'' VCP1.60%
8'' VCP
0.4%
8'' VCP
3.6%24'' VCP
0%
8'' VCP2.2%
8'' VCP3.60%
8'' VCP0%
8'' VCP
2.8%
8'' VCP
1.94%
8'' VCP
2.30%
8'' VCP0.56%
8'' VCP
0.40%
8'' VCP
0.40% 8'' VCP
0.60%
8'' VCP
0.90%
8'' VCP
1.00%
8'' VCP
0.92%
8'' VCP
0.40%
8'' VCP
1.00%
8'' VCP0.50%
8'' VCP0.60%
8'' VCP
2.20%
8'' VCP1.22%
8'' VCP
1.30%
8'' VCP0.80%
8'' VCP
4.20%8'' VCP
3.16%
8'' VCP
1.90%
8'' VCP
1.80%
8'' VCP
1.80%
8'' VCP
1.80%
8'' VCP
1.80%
8'' VCP
1.80%
8'' VCP
0.50%
8'' VCP0.40%
8'' VCP
0.40%
8'' VCP
1.36%
8'' VCP
1.36%
8'' VCP
0.60%
8'' VCP
0.8%
8'' VCP
0.60% 8'' VCP
0.60%
8'' VCP
1.36% 8'' VCP 1.36%
8'' VCP
1.36%
8'' VCP
1.60%
8'' VCP
1.60%
8'' VCP
1.57%
8'' VCP
0.40%
8'' VCP
2.70%
8'' VCP0.40%
8'' VCP
1.57%
8'' VCP
1.57%
8'' VCP
1.32%
8'' VCP
1.00%
16'' HDPE
0.50%
8'' VCP
1.00%
16'' HDPE
0.50%
16'' HDPE
0.50%
8'' VCP
1.14%
16'' HDPE
1.32%
16'' HDPE
0.84%
16'' HDPE0.85%
16'' HDPE1.32%
8'' VCP