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Project Specific Water Quality Management Plan
A Template for Projects located within the Santa Ana Watershed Region of Riverside County Project Title: Tentative Tract Map 38421, Town Center at Moreno Valley Specific Plan Development No: Insert text here
Design Review/Case No: LWQ22-0026
Original Date Prepared: 6/13/2022
Revision Date(s): 8/15/2022
9/30/2022
Prepared for Compliance with
Regional Board Order No. R8-2010-0033
Contact Information:
Prepared for: Lewis Management Corp
1156 N. Mountain Ave.
Upland, CA 91786
Prepared by: Cannon Corporation
Samuel J. Jacoby, PE, QSD
16842 Von Karman Ave
Suite 150
Irvine CA 92606
949-681-0255
Preliminary
Final
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A Brief Introduction
This Project-Specific WQMP Template for the Santa Ana Region has been prepared to help guide you in documenting compliance for your project. Because this document has been designed to specifically document compliance, you will need to utilize the WQMP Guidance Document as your “how-to” manual to help guide you through this process. Both the Template and Guidance Document go hand-in-hand, and will help facilitate a well prepared Project-Specific WQMP. Below is a flowchart for the layout of this Template that will provide the steps required to document compliance.
Section A Project and Site Information Section B Optimize Site Utilization Section C Delineate Drainage Management Areas (DMAs) Section G Source Control BMPs Section I Operation, Maintenance, and Funding Section F Hydromodification Section E Alternative Compliance Section D Implement LID BMPs Section H Construction Plan Checklist
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OWNER’S CERTIFICATION
This Project-Specific Water Quality Management Plan (WQMP) has been prepared for Lewis Management Corp. by Samuel J. Jacoby, PE, QSD, Cannon Corporation for the Tentative Tract Map 38421, Town Center at Moreno Valley Specific Plan project.
This WQMP is intended to comply with the requirements of City of Moreno Valley for Ordinance 827 which includes the requirement for the preparation and implementation of a Project-Specific WQMP.
The undersigned, while owning the property/project described in the preceding paragraph, shall be responsible for the implementation and funding of this WQMP and will ensure that this WQMP is amended as appropriate to reflect up-to-date conditions on the site. In addition, the property owner accepts responsibility for interim operation and maintenance of Stormwater BMPs until such time as this responsibility is formally transferred to a subsequent owner. This WQMP will be reviewed with the facility operator, facility supervisors, employees, tenants, maintenance and service contractors, or any other party (or parties) having responsibility for implementing portions of this WQMP. At least one copy of this WQMP will be maintained at the project site or project office in perpetuity. The undersigned is authorized to certify and to approve implementation of this WQMP. The undersigned is aware that implementation of this WQMP is enforceable under City of Moreno Valley Water Quality Ordinance (Municipal Code Section 8.10).
"I, the undersigned, certify under penalty of law that the provisions of this WQMP have been reviewed and accepted and that the WQMP will be transferred to future successors in interest." Owner’s Signature Date
Owner’s Printed Name Owner’s Title/Position
PREPARER’S CERTIFICATION
“The selection, sizing and design of stormwater treatment and other stormwater quality and quantity control measures in this plan meet the requirements of Regional Water Quality Control Board Order No. R8-2010-0033 and any subsequent amendments thereto.”
Preparer’s Signature Date
Preparer’s Printed Name Preparer’s Title/Position
Preparer’s Licensure:
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Table of Contents
Section A: Project and Site Information........................................................................................................ 6 A.1 Maps and Site Plans............................................................................................................................7 A.2 Identify Receiving Waters...................................................................................................................8 A.3 Additional Permits/Approvals required for the Project: ....................................................................9 Section B: Optimize Site Utilization (LID Principles) ................................................................................... 10 Section C: Delineate Drainage Management Areas (DMAs)....................................................................... 12 Section D: Implement LID BMPs................................................................................................................. 15 D.1 Infiltration Applicability ....................................................................................................................15 D.2 Harvest and Use Assessment............................................................................................................16 D.3 Bioretention and Biotreatment Assessment....................................................................................18 D.4 Feasibility Assessment Summaries...................................................................................................19 D.5 LID BMP Sizing ..................................................................................................................................20 Section E: Alternative Compliance (LID Waiver Program).......................................................................... 25 E.1 Identify Pollutants of Concern ..........................................................................................................26 E.2 Stormwater Credits...........................................................................................................................27 E.3 Sizing Criteria.....................................................................................................................................27 E.4 Treatment Control BMP Selection ....................................................................................................28 Section F: Hydromodification ..................................................................................................................... 29 F.1 Hydrologic Conditions of Concern (HCOC) Analysis..........................................................................29 F.2 HCOC Mitigation................................................................................................................................30 Section G: Source Control BMPs................................................................................................................. 31 Section H: Construction Plan Checklist....................................................................................................... 32 Section I: Operation, Maintenance and Funding........................................................................................ 33 - 5 -
List of Tables
Table A.1 Identification of Receiving Waters................................................................................................8 Table A.2 Other Applicable Permits..............................................................................................................9 Table C.1 DMA Classifications.....................................................................................................................12 Table C.2 Type ‘A’, Self-Treating Areas.......................................................................................................13 Table C.3 Type ‘B’, Self-Retaining Areas .....................................................................................................13 Table C.4 Type ‘C’, Areas that Drain to Self-Retaining Areas......................................................................14 Table C.5 Type ‘D’, Areas Draining to BMPs ...............................................................................................14 Table D.1 Infiltration Feasibility ..................................................................................................................15 Table D.2 LID Prioritization Summary Matrix .............................................................................................19 Table D.3 DCV Calculations for LID BMPs...................................................................................................20 Table E.1 Potential Pollutants by Land Use Type........................................................................................26 Table E.2 Water Quality Credits..................................................................................................................27 Table E.3 Treatment Control BMP Sizing ....................................................................................................27 Table E.4 Treatment Control BMP Selection ..............................................................................................28 Table F.1 Hydrologic Conditions of Concern Summary ..............................................................................29 Table G.1 Permanent and Operational Source Control Measures .............................................................31 Table H.1 Construction Plan Cross-reference.............................................................................................32 List of Appendices
Appendix 1: Maps and Site Plans................................................................................................................34 Appendix 2: Construction Plans..................................................................................................................35 Appendix 3: Soils Information.....................................................................................................................36 Appendix 4: Historical Site Conditions........................................................................................................37 Appendix 5: LID Infeasibility........................................................................................................................38 Appendix 6: BMP Design Details.................................................................................................................39 Appendix 7: Hydromodification..................................................................................................................40 Appendix 8: Source Control ........................................................................................................................41 Appendix 9: O&M .......................................................................................................................................42 Appendix 10: Educational Materials.........................................................................................................- 6 - - 6 -
Section A: Project and Site Information
PROJECT INFORMATION
Type of Project: Mixed Use, residential, commercial
Planning Area: N/A
Community Name: City of Moreno Valley
Development Name: Tentative Tract Map 38421, Town Center at Moreno Valley Specific Plan
PROJECT LOCATION
Latitude & Longitude (DMS): 33.92d N, 117.19d W
Project Watershed and Sub-Watershed: Lake Elsinore, San Jacinto River APN(s): 487-470-030, 031,
Map Book and Page No.: 11/10
PROJECT CHARACTERISTICS
Proposed or Potential Land Use(s) Residential,
Commercial
Proposed or Potential SIC Code(s) 8811,5999
Area of Impervious Project Footprint (SF) 0 SF (existing) Total Area of proposed Impervious Surfaces within the Project Limits (SF)/or Replacement 1,752,028± SF (prop’d) Does the project consist of offsite road improvements? Y N Does the project propose to construct unpaved roads? Y N Is the project part of a larger common plan of development (phased project)? Y N
EXISTING SITE CHARACTERISTICS
Total area of existing Impervious Surfaces within the project limits (SF) 0 Is the project located within any MSHCP Criteria Cell? Y N If so, identify the Cell number: N/A
Are there any natural hydrologic features on the project site? Y N Is a Geotechnical Report attached? Y N
If no Geotech. Report, list the NRCS soils type(s) present on the site (A, B, C and/or D) N/A Existing and Proposed Site Description
(Section added at request of Plan reviewer)
As described in Section B, the site exists in an undeveloped condition. There exists a single parcel between Bay Avenue and Cottonwood Avenue, and a second parcel between Cottonwood and Alessandro Boulevard. there are several minor pieces of each parcel that have been conveyed as right of way easements on the adjacent streets including Nason Street. The project proposes to vacate Bay Avenue and re-dedicate a narrower right of way; dedicate a new, north-south "A" street; create two park parcels and create 6 developable parcels. The proposed lot-specific development plans have not yet been determined. As part of this initial phase of work (mass grading, constructing temporary sedimentation basins, and common infrastructure), the project aims to identify significant restrictions or opportunities for lot-specific water quality. As each lot develops, an expected condition of approval will - 7 -
be that each lot will be required to submit an independent Water Quality Management Plan, complete with lot-specific infiltration testing. Please note that the BMPs identified herein are conceptual in nature, and are not intended for construction during the mapping/initial work, but instead will guide future development-specific BMPs.
Per plan checker for Tentative Map stage, ultimate BMPs are not sited or determined on the BMP exhibits resulting from these factors. Additionally, considerations should be taken by Engineer of Record on future phases to document actual location of sedimentation basins (in place prior to work) and take appropriate measures when siting ultimate BMPs, such as avoiding these areas, or performing additional testing.
What is the Water Quality Design Storm Depth for the project? 0.65 A.1 Maps and Site Plans
When completing your Project-Specific WQMP, include a map of the local vicinity and existing site. In addition, include all grading, drainage, landscape/plant palette and other pertinent construction plans in Appendix 2. At a minimum, your WQMP Site Plan should include the following:
• Drainage Management Areas
• Proposed Structural BMPs
• Drainage Path
• Drainage Infrastructure, Inlets, Overflows
• Source Control BMPs
• Buildings, Roof Lines, Downspouts
• Impervious Surfaces
• Standard Labeling
Use your discretion on whether or not you may need to create multiple sheets or can appropriately accommodate these features on one or two sheets. Keep in mind that the Co-Permittee plan reviewer must be able to easily analyze your project utilizing this template and its associated site plans and maps. - 8 -
A.2 Identify Receiving Waters
Using Table A.1 below, list in order of upstream to downstream, the receiving waters that the project site is tributary to. Continue to fill each row with the Receiving Water’s 303(d) listed impairments (if any), designated beneficial uses, and proximity, if any, to a RARE beneficial use. Include a map of the receiving waters in Appendix 1.
Table A.1 Identification of Receiving Waters
Receiving Waters EPA Approved 303(d) List Impairments
Designated
Beneficial Uses
Proximity to
RARE Beneficial
Use
Perris Valley Storm
Drain Channel
None N/A N/A
san jacinto river -
reaches 1,2,3 None
INTERMITTENT - MUN,
AGR, GWR,
REC1, REC2, WARM,
WILD
N/A
Canyon Lake Nutrients
MUN, AGR, GWR, REC1,
REC2, WARM,
WILD
N/A
Lake Elsinore
PCBs (Polychlorinated biphenyls)
(68444), Organic Enrichment/Low
Dissolved Oxygen (68808),
Nutrients (69206), Toxicity
(76493), DDT
(Dichlorodiphenyltrichloroethane)
(94768)
REC1, REC2, WARM,
WILD N/A
Temescal Creek,
Reach 6 None
INTERMITTENT - GWR,
REC1, REC2, WARM,
WILD
N/A
Temescal Creek,
Reach 5
None
AGR, GWR, REC1, REC2,
WARM, WILD, RARE N/A
Temescal Creek,
Reach 4
None
RARE, INTERMITTENT -
AGR, GWR, REC1, REC2,
WARM, WILD
N/A
Temescal Creek,
Reach 3
None N/A N/A
Temescal Creek,
Reach 2
None
INTERMITTENT - AGR,
IND, GWR, REC1, REC2,
LWARM, WILD
N/A
Temescal Creek,
Reach 1
None
REC1, REC2, WARM,
WILD N/A
Santa Ana River,
Reach 2 None
AGR, GWR, REC1, REC2,
WARM, WILD, RARE,
SPWN
48 Mi.
Santa Ana River,
Reach 1
None
REC1, REC2, WARM,
WILD N/A
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A.3 Additional Permits/Approvals required for the Project:
Table A.2 Other Applicable Permits
Agency Permit Required
State Department of Fish and Game, 1602 Streambed Alteration Agreement Y N State Water Resources Control Board, Clean Water Act (CWA) Section 401 Water Quality Cert. Y N US Army Corps of Engineers, CWA Section 404 Permit Y N
US Fish and Wildlife, Endangered Species Act Section 7 Biological Opinion Y N Statewide Construction General Permit Coverage Y N
Statewide Industrial General Permit Coverage Y N
Western Riverside MSHCP Consistency Approval (e.g., JPR, DBESP) Y N Other (please list in the space below as required)
City of Moreno Valley Grading Permit
Y N
If yes is answered to any of the questions above, the Co-Permittee may require proof of approval/coverage from those agencies as applicable including documentation of any associated requirements that may affect this Project-Specific WQMP. □ ~
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Section B: Optimize Site Utilization (LID Principles)
Review of the information collected in Section ‘A’ will aid in identifying the principal constraints on site design and selection of LID BMPs as well as opportunities to reduce imperviousness and incorporate LID Principles into the site and landscape design. For example, constraints might include impermeable soils, high groundwater, groundwater pollution or contaminated soils, steep slopes, geotechnical instability, high-intensity land use, heavy pedestrian or vehicular traffic, utility locations or safety concerns. Opportunities might include existing natural areas, low areas, oddly configured or otherwise unbuildable parcels, easements and landscape amenities including open space and buffers (which can double as locations for bioretention BMPs), and differences in elevation (which can provide hydraulic head). Prepare a brief narrative for each of the site optimization strategies described below. This narrative will help you as you proceed with your LID design and explain your design decisions to others.
The 2010 Santa Ana MS4 Permit further requires that LID Retention BMPs (Infiltration Only or Harvest and Use) be used unless it can be shown that those BMPs are infeasible. Therefore, it is important that your narrative identify and justify if there are any constraints that would prevent the use of those categories of LID BMPs. Similarly, you should also note opportunities that exist which will be utilized during project design. Upon completion of identifying Constraints and Opportunities, include these on your WQMP Site plan in Appendix 1.
Site Optimization
The following questions are based upon Section 3.2 of the WQMP Guidance Document. Review of the WQMP Guidance Document will help you determine how best to optimize your site and subsequently identify opportunities and/or constraints, and document compliance.
Did you identify and preserve existing drainage patterns? If so, how? If not, why? The existing site has a subtle topographic, and hydrologic, north-south aligned ridge on the eastern half of the site, that separates drainage southeast to Nason St. from flow directed southwest towards Alessandro, Bay and ultimately Morrison St. This ridge is separate from the existing soil stockpile at the southeast corner of the site. The project has 'tabled' existing and built-out hydrology from the proposed parcels according to the divide, and the water quality design follows accordingly.
Did you identify and protect existing vegetation? If so, how? If not, why? Native vegetation is not preserved. The site currently exists in an undeveloped condition, and will be mass-graded to accommodate the development
Did you identify and preserve natural infiltration capacity? If so, how? If not, why? Yes, infiltration testing has occurred, and will be maintained through limited sub-surface interaction, and limited the 'cut' in the earthwork. Infiltration is proposed for BMPs Did you identify and minimize impervious area? If so, how? If not, why? The project proposes impervious areas by zone and by tentatively mapped parcel. The project proposes immediate imperviousness solely along the project's roadways - the roadway imperviousness is - 11 -
mandated by the City of Moreno Valley. Future phases will identify and minimize imperviousness as practicable.
Did you identify and disperse runoff to adjacent pervious areas? If so, how? If not, why? The project proposes immediate imperviousness solely along the project's roadways - the roadway imperviousness is mandated by the City of Moreno Valley. Future phases will identify and minimize imperviousness as practicable.
PLEASE NOTE:
This WQMP is being prepared to support a non-development-specific tentative tract map. While the infrastructure for the development is proposed, such as roads water, sewer, improvements to adjacent rights of way, the project proposes to subdivide the land from two parcels to 8 proposed lots (inclusive of parks). The lot-specific development plans have not been prepared. Once said lot plans are developed, the developer would, consistent with City guidance, prepare lot-specific WQMP plans.
Based on the findings contained herein, infiltration appears to be feasible, and latter WQMPs are anticipated to be consistent within this overall WQMP's findings and recommendations. - 12 -
Section C: Delineate Drainage Management Areas
(DMAs)
Utilizing the procedure in Section 3.3 of the WQMP Guidance Document which discusses the methods of delineating and mapping your project site into individual DMAs, complete Table C.1 below to appropriately categorize the types of classification (e.g., Type A, Type B, etc.) per DMA for your project site. Upon completion of this table, this information will then be used to populate and tabulate the corresponding tables for their respective DMA classifications.
Table C.1 DMA Classifications
DMA Name or ID Surface Type(s)1 Area (Sq. Ft.) DMA Type DMA 1 Residential impervious 210,700 Type D-Bioinfiltratoin landscape 90,300 Type D-Bioinfiltratoin
301,000
DMA 2 Residential impervious 262,536 Type D-Bioinfiltratoin landscape 112,515 Type D-Bioinfiltratoin
375,052
DMA 3a Residential impervious 71,961 Type D-Bioinfiltratoin landscape 30,840 Type D-Bioinfiltratoin
102,802
DMA 3b Residential impervious 103,063 Type D-Bioinfiltratoin landscape 44,170 Type D-Bioinfiltratoin
147,233
DMA 4a Park impervious 15,072 Type D-Bioinfiltratoin
landscape 60,287 Type D-Bioinfiltratoin
75,359
DMA 4b Park impervious 15,420 Type D-Bioinfiltratoin
landscape 90,779 Type D-Bioinfiltratoin
106,199
DMA 5 Residential impervious 227,165 Type D-Bioinfiltratoin landscape 97,357 Type D-Bioinfiltratoin
324,522
DMA 6 Residential impervious 239,057 Type D-Bioinfiltratoin landscape 102,453 Type D-Bioinfiltratoin
341,510
DMA 7a commercial impervious 176,614 Type D-Bioinfiltratoin landscape 31,167 Type D-Bioinfiltratoin
207,781
DMA 7b commercial impervious 412,470 Type D-Bioinfiltratoin landscape 72,789 Type D-Bioinfiltratoin
485,258
DMA 8 Residential impervious 11,935 Type D-Bioinfiltratoin landscape 47,742 Type D-Bioinfiltratoin
59,677
(CONTINUED, NEXT PAGE)
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DMA Name or ID Surface Type(s)1 Area (Sq. Ft.) DMA Type DMA ROW SOUTH Street,Sidewalk 110,120 None
landscape 27,530 None
137,650
DMA ROW NORTH Street,Sidewalk 140,786 None
landscape 35,196 None
175,982
DMA ROW EAST Street,Sidewalk 177,376 None
landscape 44,344 None
221,720
1Reference Table 2-1 in the WQMP Guidance Document to populate this column Table C.2 Type ‘A’, Self-Treating Areas
DMA Name or ID Area (Sq. Ft.) Stabilization Type Irrigation Type (if any) n/a
Table C.3 Type ‘B’, Self-Retaining Areas
Note by engineer: Consistent with City comments during preliminary WQMP review, the infiltration BMPs will account for the volume of self-retaining landscape areas. While the areas may, in fact, self-retain, the City requires the infiltration BMPs to be sized in the event that self-retaining fails, or otherwise is non-functional.
Self-Retaining Area
Type ‘C’ DMAs that are draining to the Self-Retaining
Area
DMA
Name/ ID
Post-project
surface type
Area
(square
feet)
Storm
Depth
(inches) DMA Name /
ID
[C] from Table C.4
=
Required Retention Depth
(inches)
[A] [B] [C] [D]
TBD (DEFERRED UNTIL SITE-SPECIFIC WQMPs)* TBD (DEFERRED UNTIL SITE-SPECIFIC WQMPs)* *Tables left blank resulting from direction of plan checker during tentative map stage. 1-
~
r--
B · C
[D] = [B] + [A]
I
I
-
-
-
- I
I --i
-
-
I _J
- I
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Table C.4 Type ‘C’, Areas that Drain to Self-Retaining Areas DMA Receiving Self-Retaining DMA DMA Name/ ID Area (square feet) Post-project surface type Runoff factor Product
DMA name /ID
Area (square
feet) Ratio
[A] [B] [C] = [A] x [B] [D] [C]/[D]
Table C.5 Type ‘D’, Areas Draining to BMPs
DMA Name or ID BMP Name or ID
DMA 1 BMP 1, TBD
DMA 2 BMP 2, TBD
DMA 3a BMP 3a, TBD
DMA 3b BMP 3b, TBD
DMA 4a BMP 4a, TBD
DMA 4b BMP 4b, TBD
DMA 5 BMP 5, TBD
DMA 6 BMP 6, TBD
DMA 7a BMP 7a, TBD
DMA 7b BMP 7b, TBD
DMA 8 BMP 8, TBD
DMA ROW(all) N/A
Note: More than one drainage management area can drain to a single LID BMP, however, one drainage management area may not drain to more than one BMP. - 15 -
Section D: Implement LID BMPs
D.1 Infiltration Applicability
Is there an approved downstream ‘Highest and Best Use’ for stormwater runoff (see discussion in Chapter 2.4.4 of the WQMP Guidance Document for further details)? Y N If yes has been checked, Infiltration BMPs shall not be used for the site. If no, continue working through this section to implement your LID BMPs. It is recommended that you contact your Co-Permittee to verify whether or not your project discharges to an approved downstream ‘Highest and Best Use’ feature.
Geotechnical Report
A Geotechnical Report or Phase I Environmental Site Assessment may be required by the Copermittee to confirm present and past site characteristics that may affect the use of Infiltration BMPs. In addition, the Co-Permittee, at their discretion, may not require a geotechnical report for small projects as described in Chapter 2 of the WQMP Guidance Document. If a geotechnical report has been prepared, include it in Appendix 3. In addition, if a Phase I Environmental Site Assessment has been prepared, include it in Appendix 4.
Is this project classified as a small project consistent with the requirements of Chapter 2 of the WQMP Guidance Document? Y N
Infiltration Feasibility
Table D.1 below is meant to provide a simple means of assessing which DMAs on your site support Infiltration BMPs and is discussed in the WQMP Guidance Document in Chapter 2.4.5. Check the appropriate box for each question and then list affected DMAs as applicable. If additional space is needed, add a row below the corresponding answer.
Table D.1 Infiltration Feasibility
Does the project site… YES NO
…have any DMAs with a seasonal high groundwater mark shallower than 10 feet? XX If Yes, list affected DMAs:
…have any DMAs located within 100 feet of a water supply well? XX If Yes, list affected DMAs:
…have any areas identified by the geotechnical report as posing a public safety risk where infiltration of stormwater could have a negative impact?
XX
If Yes, list affected DMAs:
…have measured in-situ infiltration rates of less than 1.6 inches / hour? XX If Yes, list affected DMAs:
…have significant cut and/or fill conditions that would preclude in-situ testing of infiltration rates at the final infiltration surface?
XX
If Yes, list affected DMAs:
…geotechnical report identify other site-specific factors that would preclude effective and safe infiltration? XX Describe here:
If you answered “Yes” to any of the questions above for any DMA, Infiltration BMPs should not be used for those DMAs and you should proceed to the assessment for Harvest and Use below.
Note by engineer: Consistent with City comments during preliminary WQMP review, wile the geotechnical report did indicated infiltration feasibility during the Tentative Map stage, each lot- □ ~
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specific WQMP will be required to submit Lot-Specific geotechnical analysis and infiltration testing. The lot-specific WQMP shall be based on the subsequent test results.
D.2 Harvest and Use Assessment
Please check what applies:
Reclaimed water will be used for the non-potable water demands for the project.
Downstream water rights may be impacted by Harvest and Use as approved by the Regional Board (verify with the Copermittee).
The Design Capture Volume will be addressed using Infiltration Only BMPs. In such a case, Harvest and Use BMPs are still encouraged, but it would not be required if the Design Capture Volume will be infiltrated or evapotranspired.
If any of the above boxes have been checked, Harvest and Use BMPs need not be assessed for the site. If neither of the above criteria applies, follow the steps below to assess the feasibility of irrigation use, toilet use and other non-potable uses (e.g., industrial use).
Irrigation Use Feasibility
Complete the following steps to determine the feasibility of harvesting stormwater runoff for Irrigation Use BMPs on your site:
Step 1: Identify the total area of irrigated landscape on the site, and the type of landscaping used.
Total Area of Irrigated Landscape: N/A, infiltration and/or bioretention proposed Type of Landscaping (Conservation Design or Active Turf): N/A, infiltration and/or bioretention proposed
Step 2: Identify the planned total of all impervious areas on the proposed project from which runoff might be feasibly captured and stored for irrigation use. Depending on the configuration of buildings and other impervious areas on the site, you may consider the site as a whole, or parts of the site, to evaluate reasonable scenarios for capturing and storing runoff and directing the stored runoff to the potential use(s) identified in Step 1 above.
Total Area of Impervious Surfaces: N/A, infiltration and/or bioretention proposed Step 3: Cross reference the Design Storm depth for the project site (see Exhibit A of the WQMP Guidance Document) with the left column of Table 2-3 in Chapter 2 to determine the minimum area of Effective Irrigated Area per Tributary Impervious Area (EIATIA).
Enter your EIATIA factor: N/A, infiltration and/or bioretention proposed Step 4: Multiply the unit value obtained from Step 3 by the total of impervious areas from Step 2 to develop the minimum irrigated area that would be required.
Minimum required irrigated area: N/A, infiltration and/or bioretention proposed Step 5: Determine if harvesting stormwater runoff for irrigation use is feasible for the project by comparing the total area of irrigated landscape (Step 1) to the minimum required irrigated area (Step 4).
Minimum required irrigated area (Step 4) Available Irrigated Landscape (Step 1) N/A, infiltration and/or bioretention proposed N/A, infiltration and/or bioretention proposed
□
□
[gl
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Toilet Use Feasibility
Complete the following steps to determine the feasibility of harvesting stormwater runoff for toilet flushing uses on your site:
Step 1: Identify the projected total number of daily toilet users during the wet season, and account for any periodic shut downs or other lapses in occupancy:
Projected Number of Daily Toilet Users: N/A, infiltration and/or bioretention proposed Project Type: N/A, infiltration and/or bioretention proposed Step 2: Identify the planned total of all impervious areas on the proposed project from which runoff might be feasibly captured and stored for toilet use. Depending on the configuration of buildings and other impervious areas on the site, you may consider the site as a whole, or parts of the site, to evaluate reasonable scenarios for capturing and storing runoff and directing the stored runoff to the potential use(s) identified in Step 1 above.
Total Area of Impervious Surfaces: N/A, infiltration and/or bioretention proposed Step 3: Enter the Design Storm depth for the project site (see Exhibit A) into the left column of Table 2-1 in Chapter 2 to determine the minimum number or toilet users per tributary impervious acre (TUTIA).
Enter your TUTIA factor: N/A, infiltration and/or bioretention proposed Step 4: Multiply the unit value obtained from Step 3 by the total of impervious areas from Step 2 to develop the minimum number of toilet users that would be required.
Minimum number of toilet users: N/A, infiltration and/or bioretention proposed Step 5: Determine if harvesting stormwater runoff for toilet flushing use is feasible for the project by comparing the Number of Daily Toilet Users (Step 1) to the minimum required number of toilet users (Step 4).
Minimum required Toilet Users (Step 4) Projected number of toilet users (Step 1) N/A, infiltration and/or bioretention
proposed
N/A, infiltration and/or bioretention
proposed
Other Non-Potable Use Feasibility
Are there other non-potable uses for stormwater runoff on the site (e.g. industrial use)? See Chapter 2 of the Guidance for further information. If yes, describe below. If no, write N/A.
N/A, infiltration and/or bioretention proposed
Step 1: Identify the projected average daily non-potable demand, in gallons per day, during the wet season and accounting for any periodic shut downs or other lapses in occupancy or operation.
Average Daily Demand: N/A, infiltration and/or bioretention proposed Step 2: Identify the planned total of all impervious areas on the proposed project from which runoff might be feasibly captured and stored for the identified non-potable use. Depending on the configuration of buildings and other impervious areas on the site, you may consider the site as a whole, or parts of the site, to evaluate reasonable scenarios for capturing and storing runoff and directing the stored runoff to the potential use(s) identified in Step 1 above. - 18 -
Total Area of Impervious Surfaces: N/A, infiltration and/or bioretention proposed Step 3: Enter the Design Storm depth for the project site (see Exhibit A) into the left column of Table 2-3 in Chapter 2 to determine the minimum demand for non-potable uses per tributary impervious acre.
Enter the factor from Table 2-3: N/A, infiltration and/or bioretention proposed Step 4: Multiply the unit value obtained from Step 4 by the total of impervious areas from Step 3 to develop the minimum number of gallons per day of non-potable use that would be required.
Minimum required use: N/A, infiltration and/or bioretention proposed Step 5: Determine if harvesting stormwater runoff for other non-potable use is feasible for the project by comparing the Number of Daily Toilet Users (Step 1) to the minimum required number of toilet users (Step 4).
Minimum required non-potable use (Step 4) Projected average daily use (Step 1) N/A, infiltration and/or bioretention proposed N/A, infiltration and/or bioretention proposed
If Irrigation, Toilet and Other Use feasibility anticipated demands are less than the applicable minimum values, Harvest and Use BMPs are not required and you should proceed to utilize LID Bioretention and Biotreatment, unless a site-specific analysis has been completed that demonstrates technical infeasibility as noted in D.3 below.
D.3 Bioretention and Biotreatment Assessment
Other LID Bioretention and Biotreatment BMPs as described in Chapter 2.4.7 of the WQMP Guidance Document are feasible on nearly all development sites with sufficient advance planning.
Select one of the following:
LID Bioretention/Biotreatment BMPs will be used for some or all DMAs of the project as noted below in Section D.4 (note the requirements of Section 3.4.2 in the WQMP Guidance Document).
A site-specific analysis demonstrating the technical infeasibility of all LID BMPs has been performed and is included in Appendix 5. If you plan to submit an analysis demonstrating the technical infeasibility of LID BMPs, request a pre-submittal meeting with the Copermittee to discuss this option. Proceed to Section E to document your alternative compliance measures. □
□
- 19 -
D.4 Feasibility Assessment Summaries
From the Infiltration, Harvest and Use, Bioretention and Biotreatment Sections above, complete Table D.2 below to summarize which LID BMPs are technically feasible, and which are not, based upon the established hierarchy.
Table D.2 LID Prioritization Summary Matrix
DMA Name/ID
LID BMP Hierarchy No LID
(Alternative
1. Infiltration 2. Harvest and use 3. Bioretention 4. Biotreatment Compliance) DMA 1
DMA 2
DMA 3a
DMA 3b
DMA 4a
DMA 4b
DMA 5
DMA 6
DMA 7a
DMA 7b
DMA 8
DMA ROW
Note by engineer: The conceptual "Bio-Infiltration" is an alias to Infiltration Basins, per the Riverside County BMP Manual, and is not intended to be interpreted as "Bioretention" which does allow for piped discharge of treated flow.
For those DMAs where LID BMPs are not feasible, provide a brief narrative below summarizing why they are not feasible, include your technical infeasibility criteria in Appendix 5, and proceed to Section E below to document Alternative Compliance measures for those DMAs. Recall that each proposed DMA must pass through the LID BMP hierarchy before alternative compliance measures may be considered.
The right of way has not been identified as containing, nor draining to, a BMP. ~ □ □ □ □
~ □
~ □
~ □
~ □
~ □
~ □
~ □
~ □
~ □
~ □
□ □ □ □ ~
- 20 -
D.5 LID BMP Sizing
Each LID BMP must be designed to ensure that the Design Capture Volume will be addressed by the selected BMPs. First, calculate the Design Capture Volume for each LID BMP using the VBMP worksheet in Appendix F of the LID BMP Design Handbook. Second, design the LID BMP to meet the required VBMP using a method approved by the Copermittee. Utilize the worksheets found in the LID BMP Design Handbook or consult with your Copermittee to assist you in correctly sizing your LID BMPs. Complete Table D.3 below to document the Design Capture Volume and the Proposed Volume for each LID BMP.
Provide the completed design procedure sheets for each LID BMP in Appendix 6. You may add additional rows to the table below as needed.
Table D.3 DCV Calculations for LID BMPs
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 1
301,000 Residential 0.7 0.493894
148,661.90
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=300999.6 Σ=148662 0.66 8,176.4
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 2
375,052 Residential 0.7 0.493894
185,235.73
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=375051.6 Σ=185236 0.66 10,188.0
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Enter BMP Name / Identifier
Here
I I I
I
I I I
- 21 -
[A] [B] [C] [A] x [C]
DMA 3a
102,802 Residential 0.7 0.493894
50,773.09
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=102801.6 Σ=50773 0.66 2,792.5
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 3b
147,233 Residential 0.7 0.493894
72,717.40
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=147232.8 Σ=72717 0.66 3,999.5
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 4a
75,359 Residential 0.2 0.170464
12,845.96
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=75358.8 Σ=12846 0.66 706.5
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 4b Residential 0.2 0.170464 Design Design Proposed
I I I
I I I
I I I
I I I I
- 22 -
77,101 13,142.98 Storm
Depth
(in)
Capture
Volume,
VBMP
(cubic
feet)
Volume
on Plans
(cubic
feet)
AT
Σ=77101.2 Σ=13143 0.66 722.9
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 5
324,522 Residential 0.7 0.493894
160,279.47
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=324522 Σ=160279 0.66 8,815.4
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 6
341,510 Residential 0.7 0.493894
168,669.94
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=341510.4 Σ=168670 0.66 9,276.8
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 7a
207,781 Residential 0.85 0.66126925
137,399.32
Design
Storm
Depth
Design
Capture
Volume,
Proposed
Volume
on Plans
I I I
I I I
I I I
- 23 -
(in) VBMP
(cubic
feet)
(cubic
feet)
AT
Σ=207781.2 Σ=137399 0.66 7,557.0
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA 8
59,677 Commercial 0.2 0.170464
10,172.81
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=59677.2 Σ=10173 0.66 559.5
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA
ROW
SOUTH
137,650 Right of Way 0.7
0.493894
67,984.31
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=137649.6 Σ=67984 0.66 3,739.1
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA
ROW
NORTH
175,982 Right of Way 0.7
0.493894
86,916.65 Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
I I I
- 24 -
AT
Σ=175982.4 Σ=86917 0.66 4,780.4
DMA
Type/ID
DMA Area
(square
feet)
Post-Project
Surface Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor Enter BMP Name / Identifier
Here
[A] [B] [C] [A] x [C]
DMA
ROW
EAST
221,720 Right of Way 0.7
0.493894
109,506.38
Design
Storm
Depth
(in)
Design
Capture
Volume,
VBMP
(cubic
feet)
Proposed
Volume
on Plans
(cubic
feet)
AT
Σ=221720.4 Σ=109506 0.66 6,022.9
[B], [C] is obtained as described in Section 2.3.1 of the WQMP Guidance Document [E] is obtained from Exhibit A in the WQMP Guidance Document [G] is obtained from a design procedure sheet, such as in LID BMP Design Handbook and placed in Appendix 6 - 25 -
Section E: Alternative Compliance (LID Waiver Program)
LID BMPs are expected to be feasible on virtually all projects. Where LID BMPs have been demonstrated to be infeasible as documented in Section D, other Treatment Control BMPs must be used (subject to LID waiver approval by the Copermittee). Check one of the following Boxes:
☐ LID Principles and LID BMPs have been incorporated into the site design to fully address all Drainage Management Areas. No alternative compliance measures are required for this project and thus this Section is not required to be completed.
- Or -
☒ The following Drainage Management Areas are unable to be addressed using LID BMPs. A site-specific analysis demonstrating technical infeasibility of LID BMPs has been approved by the Co-Permittee and included in Appendix 5. Additionally, no downstream regional and/or subregional LID BMPs exist or are available for use by the project. The following alternative compliance measures on the following pages are being implemented to ensure that any pollutant loads expected to be discharged by not incorporating LID BMPs, are fully mitigated.
The right of way does not drain to a BMP.
- 26 -
E.1 Identify Pollutants of Concern
Utilizing Table A.1 from Section A above which noted your project’s receiving waters and their associated EPA approved 303(d) listed impairments, cross reference this information with that of your selected Priority Development Project Category in Table E.1 below. If the identified General Pollutant Categories are the same as those listed for your receiving waters, then these will be your Pollutants of Concern and the appropriate box or boxes will be checked on the last row. The purpose of this is to document compliance and to help you appropriately plan for mitigating your Pollutants of Concern in lieu of implementing LID BMPs.
Table E.1 Potential Pollutants by Land Use Type
Priority Development
Project Categories and/or
Project Features (check those
that apply)
General Pollutant Categories
Bacterial
Indicators Metals Nutrients Pesticides
Toxic
Organic
Compounds
Sediments Trash &
Debris
Oil &
Grease
Detached Residential
Development P N P P N P P P
Attached Residential
Development P N P P N P P P(2)
Commercial/Industrial
Development P(3) P P(1) P(1) P(5) P(1) P P
Automotive Repair
Shops N P N N P(4, 5) N P P
Restaurants
(>5,000 ft2)
P N N N N N P P
Hillside Development
(>5,000 ft2)
P N P P N P P P
Parking Lots
(>5,000 ft2)
P(6) P P(1) P(1) P(4) P(1) P P
Retail Gasoline Outlets N P N N P N P P
Project Priority Pollutant(s)
of Concern
P = Potential
N = Not Potential
(1) A potential Pollutant if non-native landscaping exists or is proposed onsite; otherwise not expected (2) A potential Pollutant if the project includes uncovered parking areas; otherwise not expected (3) A potential Pollutant is land use involving animal waste (4) Specifically petroleum hydrocarbons
(5) Specifically solvents
(6) Bacterial indicators are routinely detected in pavement runoff ~
~
~
□
~
□
~
□
~ ~ ~ ~ ~ ~ ~ ~
- 27 -
E.2 Stormwater Credits
Projects that cannot implement LID BMPs but nevertheless implement smart growth principles are potentially eligible for Stormwater Credits. Utilize Table 3-8 within the WQMP Guidance Document to identify your Project Category and its associated Water Quality Credit. If not applicable, write N/A.
Table E.2 Water Quality Credits
Qualifying Project Categories Credit Percentage2
N/A
Total Credit Percentage1
1Cannot Exceed 50%
2Obtain corresponding data from Table 3-8 in the WQMP Guidance Document E.3 Sizing Criteria
After you appropriately considered Stormwater Credits for your project, utilize Table E.3 below to appropriately size them to the DCV, or Design Flow Rate, as applicable. Please reference Chapter 3.5.2 of the WQMP Guidance Document for further information.
Table E.3 Treatment Control BMP Sizing
DMA
Type/ID
DMA
Area
(square
feet)
PostProject
Surface
Type
Effective
Impervious
Fraction, If
DMA
Runoff
Factor
DMA
Area x
Runoff
Factor
Enter BMP Name / Identifier Here
[A] [B] [C] [A] x [C]
N/A
Design
Storm
Depth
(in)
Minimum
Design
Capture
Volume or
Design Flow
Rate (cubic
feet or cfs)
Total Storm
Water
Credit %
Reduction
Proposed
Volume
or Flow
on Plans
(cubic
feet or
cfs)
AT =
Σ[A] Σ= [D] [E] [F] X (1-[H]) [I]
[B], [C] is obtained as described in Section 2.3.1 from the WQMP Guidance Document [E] is obtained from Exhibit A in the WQMP Guidance Document [G] is for Flow-Based Treatment Control BMPs [G] = 43,560, for Volume-Based Control Treatment BMPs, [G] = 12 [H] is from the Total Credit Percentage as Calculated from Table E.2 above [I] as obtained from a design procedure sheet from the BMP manufacturer and should be included in Appendix 6 [F] =
- 28 -
E.4 Treatment Control BMP Selection
Treatment Control BMPs typically provide proprietary treatment mechanisms to treat potential pollutants in runoff, but do not sustain significant biological processes. Treatment Control BMPs must have a removal efficiency of a medium or high effectiveness as quantified below:
• High: equal to or greater than 80% removal efficiency • Medium: between 40% and 80% removal efficiency
Such removal efficiency documentation (e.g., studies, reports, etc.) as further discussed in Chapter 3.5.2 of the WQMP Guidance Document, must be included in Appendix 6. In addition, ensure that proposed Treatment Control BMPs are properly identified on the WQMP Site Plan in Appendix 1.
Table E.4 Treatment Control BMP Selection
Selected Treatment Control BMP
Name or ID1
Priority Pollutant(s) of
Concern to Mitigate2
Removal Efficiency
Percentage3
N/A
1 Treatment Control BMPs must not be constructed within Receiving Waters. In addition, a proposed Treatment Control BMP may be listed more than once if they possess more than one qualifying pollutant removal efficiency. 2 Cross Reference Table E.1 above to populate this column. 3 As documented in a Co-Permittee Approved Study and provided in Appendix 6. - 29 -
Section F: Hydromodification
F.1 Hydrologic Conditions of Concern (HCOC) Analysis
Once you have determined that the LID design is adequate to address water quality requirements, you will need to assess if the proposed LID Design may still create a HCOC. Review Chapters 2 and 3 (including Figure 3-7) of the WQMP Guidance Document to determine if your project must mitigate for Hydromodification impacts. If your project meets one of the following criteria which will be indicated by the check boxes below, you do not need to address Hydromodification at this time. However, if the project does not qualify for Exemptions 1, 2 or 3, then additional measures must be added to the design to comply with HCOC criteria. This is discussed in further detail below in Section F.2.
HCOC EXEMPTION 1: The Priority Development Project disturbs less than one acre. The Copermittee has the discretion to require a Project-Specific WQMP to address HCOCs on projects less than one acre on a case by case basis. The disturbed area calculation should include all disturbances associated with larger common plans of development.
Does the project qualify for this HCOC Exemption? Y N
If Yes, HCOC criteria do not apply.
HCOC EXEMPTION 2: The volume and time of concentration1 of storm water runoff for the postdevelopment condition is not significantly different from the pre-development condition for a 2-year return frequency storm (a difference of 5% or less is considered insignificant) using one of the following methods to calculate:
• Riverside County Hydrology Manual
• Technical Release 55 (TR-55): Urban Hydrology for Small Watersheds (NRCS 1986), or derivatives thereof, such as the Santa Barbara Urban Hydrograph Method • Other methods acceptable to the Co-Permittee
Does the project qualify for this HCOC Exemption? Y N
If Yes, report results in Table F.1 below and provide your substantiated hydrologic analysis in Appendix 7.
Table F.1 Hydrologic Conditions of Concern Summary
2 year – 24 hour –
Pre-condition Post-condition % Difference
Time of
Concentration
INSERT VALUE INSERT VALUE INSERT VALUE
Volume (Cubic Feet) INSERT VALUE INSERT VALUE INSERT VALUE □
□
- 30 -
1 Time of concentration is defined as the time after the beginning of the rainfall when all portions of the drainage basin are contributing to flow at the outlet.
HCOC EXEMPTION 3: All downstream conveyance channels to an adequate sump (for example, Prado Dam, Lake Elsinore, Canyon Lake, Santa Ana River, or other lake, reservoir or naturally erosion resistant feature) that will receive runoff from the project are engineered and regularly maintained to ensure design flow capacity; no sensitive stream habitat areas will be adversely affected; or are not identified on the Co-Permittees Hydromodification Sensitivity Maps.
Does the project qualify for this HCOC Exemption? Y N
If Yes, HCOC criteria do not apply and note below which adequate sump applies to this HCOC qualifier:
The western portion of the site is exempt from hydromodification per the 2012 Hydromodification Applicability Map. The eastern portion of the site was not exempt per the 2012 map, but the Current MDP map indicates that the eastern portion drains to an improved line "F:
F.2 HCOC Mitigation
If none of the above HCOC Exemption Criteria are applicable, HCOC criteria is considered mitigated if they meet one of the following conditions:
a. Additional LID BMPS are implemented onsite or offsite to mitigate potential erosion or habitat impacts as a result of HCOCs. This can be conducted by an evaluation of site-specific conditions utilizing accepted professional methodologies published by entities such as the California Stormwater Quality Association (CASQA), the Southern California Coastal Water Research Project (SCCRWP), or other Co-Permittee approved methodologies for site-specific HCOC analysis.
b. The project is developed consistent with an approved Watershed Action Plan that addresses HCOC in Receiving Waters.
c. Mimicking the pre-development hydrograph with the post-development hydrograph, for a 2- year return frequency storm. Generally, the hydrologic conditions of concern are not significant, if the post-development hydrograph is no more than 10% greater than pre-development hydrograph. In cases where excess volume cannot be infiltrated or captured and reused, discharge from the site must be limited to a flow rate no greater than 110% of the predevelopment 2-year peak flow.
Be sure to include all pertinent documentation used in your analysis of the items a, b or c in Appendix 7. ~ □
- 31 -
Section G: Source Control BMPs
Source control BMPs include permanent, structural features that may be required in your project plans — such as roofs over and berms around trash and recycling areas — and Operational BMPs, such as regular sweeping and “housekeeping”, that must be implemented by the site’s occupant or user. The MEP standard typically requires both types of BMPs. In general, Operational BMPs cannot be substituted for a feasible and effective permanent BMP. Using the Pollutant Sources/Source Control Checklist in Appendix 8, review the following procedure to specify Source Control BMPs for your site:
1. Identify Pollutant Sources: Review Column 1 in the Pollutant Sources/Source Control Checklist.
Check off the potential sources of Pollutants that apply to your site.
2. Note Locations on Project-Specific WQMP Exhibit: Note the corresponding requirements listed in Column 2 of the Pollutant Sources/Source Control Checklist. Show the location of each Pollutant source and each permanent Source Control BMP in your Project-Specific WQMP Exhibit located in Appendix 1.
3. Prepare a Table and Narrative: Check off the corresponding requirements listed in Column 3 in the Pollutant Sources/Source Control Checklist. In the left column of Table G.1 below, list each potential source of runoff Pollutants on your site (from those that you checked in the Pollutant Sources/Source Control Checklist). In the middle column, list the corresponding permanent, Structural Source Control BMPs (from Columns 2 and 3 of the Pollutant Sources/Source Control Checklist) used to prevent Pollutants from entering runoff. Add additional narrative in this column that explains any special features, materials or methods of construction that will be used to implement these permanent, Structural Source Control BMPs.
4. Identify Operational Source Control BMPs: To complete your table, refer once again to the Pollutant Sources/Source Control Checklist. List in the right column of your table the Operational BMPs that should be implemented as long as the anticipated activities continue at the site. Copermittee stormwater ordinances require that applicable Source Control BMPs be implemented; the same BMPs may also be required as a condition of a use permit or other revocable Discretionary Approval for use of the site.
Table G.1 Permanent and Operational Source Control Measures Potential Sources of Runoff
pollutants
Permanent Structural
Source Control BMPs
Operational Source Control BMPs
Trash & Debris/ Sedimentation Trash Inlet Filters
Trash & Debris/ Sedimentation Street Sweeping
Trash & Debris/ Sedimentation Storm Drain Stenciling
Trash & Debris/ Sedimentation Restrict outdoor storage
Trash & Debris/ Sedimentation Maintain trash and debris storage areas Runoff Reduction Efficient Irrigation
Trash & Debris/ Sedimentation Maintain Dock Aras
- 32 -
Section H: Construction Plan Checklist
Populate Table H.1 below to assist the plan checker in an expeditious review of your project. The first two columns will contain information that was prepared in previous steps, while the last column will be populated with the corresponding plan sheets. This table is to be completed with the submittal of your final Project-Specific WQMP.
Table H.1 Construction Plan Cross-reference
BMP No. or ID BMP Identifier and Description Corresponding Plan Sheet(s) BMP 1 Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 2 Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 3a Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 3b Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 4a Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 4b Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 5 Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 6 Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 7a Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 7b Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP BMP 8 Infiltration and/or bioretention To be designed with sitedevelopment-specific WQMP Note that the updated table — or Construction Plan WQMP Checklist — is only a reference tool to facilitate an easy comparison of the construction plans to your Project-Specific WQMP. Co-Permittee staff can advise you regarding the process required to propose changes to the approved Project-Specific WQMP.
- 34 -
Section I: Operation, Maintenance and Funding
The Copermittee will periodically verify that Stormwater BMPs on your site are maintained and continue to operate as designed. To make this possible, your Copermittee will require that you include in Appendix 9 of this Project-Specific WQMP:
1. A means to finance and implement facility maintenance in perpetuity, including replacement cost.
2. Acceptance of responsibility for maintenance from the time the BMPs are constructed until responsibility for operation and maintenance is legally transferred. A warranty covering a period following construction may also be required.
3. An outline of general maintenance requirements for the Stormwater BMPs you have selected.
4. Figures delineating and designating pervious and impervious areas, location, and type of Stormwater BMP, and tables of pervious and impervious areas served by each facility. Geolocating the BMPs using a coordinate system of latitude and longitude is recommended to help facilitate a future statewide database system.
5. A separate list and location of self-retaining areas or areas addressed by LID Principles that do not require specialized O&M or inspections but will require typical landscape maintenance as noted in Chapter 5, pages 85-86, in the WQMP Guidance. Include a brief description of typical landscape maintenance for these areas.
Your local Co-Permittee will also require that you prepare and submit a detailed Stormwater BMP Operation and Maintenance Plan that sets forth a maintenance schedule for each of the Stormwater BMPs built on your site. An agreement assigning responsibility for maintenance and providing for inspections and certification may also be required.
Details of these requirements and instructions for preparing a Stormwater BMP Operation and Maintenance Plan are in Chapter 5 of the WQMP Guidance Document.
Maintenance Mechanism: Insert text here.
Will the proposed BMPs be maintained by a Home Owners’ Association (HOA) or Property Owners Association (POA)?
Y N
Include your Operation and Maintenance Plan and Maintenance Mechanism in Appendix 9. Additionally, include all pertinent forms of educational materials for those personnel that will be maintaining the proposed BMPs within this Project-Specific WQMP in Appendix 10. □
- 35 -
Appendix 1: Maps and Site Plans
Location Map, WQMP Site Plan and Receiving Waters Map
TRACT 38421 PRELIMINARY
WATER QUALITY EXHIBIT
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
,
E
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DATE!l/21/2022
JOB NO. 211203
CPN: PEN22-077
TTM: 38421
5- SHEET
N 1156 NORTH MOUNTAIN AVENUE
UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY 0 1 INCH 1 00 FEET J TEL: (909) 985-0971
.;:L _________________________________________________________________________________ CALIFORNIA w bJ 1
_1 ______________ __JL_ ______________ .....L ___________________________ ....1... ___ ....:.... _ __J
TOWN CENTER AT MORENO VALLEY
TRACT 38421
WATER QUALITY DETAILS
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
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PLAN PREPARED BY:
5•
(TYP) TO PONDING DEPTH
J" l',EIR DEPTH MIN
DIRECT OVERFLOW DISCHARGE PER TO
STORM DRAIN CONVEYANCE. INSTALL
BENDS AS NECESSARY FOR
CONNECTION
OVERFLOW DRAIN: 6" DIA. PVC PIPE
WITH ATRIUM GATE INLET AT 4" ABOVE
FINISH GRADE
OB ERVATION 1',ELL/SDR 35
0 RFLOW STANDPIPE W/NDS
GR TE ELEVATION (T.G.)
(PE PLAN)
MULCH
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---,---2•-o• MINI-. --
APPROVED GEOTECHN
':--,: ~ ' :--,:
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1. AT LEAST 18 INCHES SHALL BE PRO\nDED BETl',£EN THE
PLANTING SURFACE AND THE CREST OF EACH PLANTER
2. PLANTERS SHALL NOT BE GRADED INTERNALLY WITH UNEVEN OR SLOPED SURFACES.
3. TOP SOIL/PLANTING MIX IS AT LEAST 24" DEEP.
4. TOP SOIL CONTAINS NO MORE THAN JO% COMPOST.
5. MINIMUM GRAVEL LAYER SHALL BE 24" DEEP.
6. DIRECT OVERFLOW DISCHARGE PER SHALL DISCHARGE TO THE STORM CONVEYANCE PIPE WITH MIN. SLOPE OF 0.5%.
7. SEE PLANTERS BOX FACT SHEET (LID ORDINANCE #181899) FOR MORE INFORMATION.
8. PLANTER WALLS PER BUILDING PLANS. EXPOSED WALLS TO
MATCH BUILDING.
9. LANDSCAPE PLANTINGS SHALL BE PER LANDSCAPE PLANS.
10. PLANTER BOX LOCATION AS SHOWN ON PLANS.
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DRAIN PIPE
6" PERF. DRAIN MIN
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BUILDING/PLANTER FOOTING
PER SEPARATE PLAN
10' O.C. LONGITUDINAL MANIFOLD 4"
DIA. PVC PERFORATED COLLECTION
PIPE WRAPED IN NON-WOVEN
GEOTEXTILE MEMBRANE PER PROJECT
PLANS
SECTION
NOT TO SCALE
PLAN PREPARED FOR:
---------< 1 CONCEPTUAL BMP 0
SEE NOTE BELOW NTS
BIORETENTION BMP CONCEPllJAL IN NAllJRE. FINAL SIZE, LOCATION,
AND BMP TYPE (FILTRATION, RETENTION, SUB SURFACE INFILTRATION) IS DEPENDANT ON LOT-SPECIFIC BMPs AS WELL AS LOT-SPECIFIC
INFILTRATION FEASIBILITY ANALYSIS
f Cannon LEWIS MANAGEMENT CORP.
~ CITY OF MORENO VALLEY
1156 NORTH MOUNTAIN AVENUE
UPLAND, CALIFORNIA 91785-0670
TEL: (909) 985-D971
DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 3B421
SHEET
2 J CALIFORNIA w Q 2
s:~--------------------------------------------------------------------------------------~---------------~----------------~----------------------------~------~ - 33 -
Appendix 2: Construction Plans
Grading and Drainage Plans
NASON STREET
A L E S S A N D R O B O U L E V A R D
COTTONWOOD AVENUE
BAY AVENUE A STREET A STREET NASON STREET
PARCEL 2
PARCEL 1
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
A
NO. 9584
ARON P. TILLMAN
S
P
R
O
FESSIONAL LAND SURVEY
O
R
STA TE OF CA LIFORNIA
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
PRELIMINARY GRADING PLAN
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LEGAL DESCRIPTION: LEGEND AND ABBREVIATIONS PREL Y GRADING PIAN FOR
THE LAND IS SITIJATED IN THE CITY OF MORENO VALLEY,
COUNTY OF RIVERSIDE, STATE OF CALIFORNIA, AND IS
DESCRIBED AS FOLLOWS:
PARCEL A: APN 487 470 31
21.94 ACRES M/L IN POR LOTS 2 & 8 BLK 93 AND LOT
7 BLK 93 MB 011/010 SB BEAR VALLEY&: ALESSANDRO
DEVELOPMENT CO LOT 2 BLOCK 93 SUBDIVISIONNAME
BEAR VALLEY & ALESSANDRO DEVELOPMENT CO ACRES
021.94 M/L LOT TYPE LOT REC MAP TYPE MAP BOOK
RECORDED CO CODE SB MAP PLAT B 011 MAP PLAT P
010 PORTION LOT PORTION LOT 7 LOT TYPE LOT PORTION
LOT PORTION LOT 8 LOT TYPE LOT
PARCEL B· APN 487 470 30
34.48 ACRES M/L IN POR LOTS 1 & 8 BLK 104 AND
LOTS 2 & 7 BLK 104 MB 011/010 SB BEAR VALLEY &
ALESSANDRO DEVELOPMENT CO LOT 1 BLOCK 104
SUBDIVISION NAME BEAR VALLEY &: ALESSANDRO
DEVELOPMENT CO ACRES 034.48 M/L LOT TYPE LOT REC
MAP TYPE MAP BOOK RECORDED CO CODE SB MAP PLAT
B 011 MAP PLAT P 010 PORTION LOT PORTION LOT 2
LOT TYPE LOT PORTION LOT PORTION LOT 7 LOT TYPE
LOT LOT 8 LOT TYPE LOT
FLOOD ZONE:
ZONE X - AREAS DETERMINED TO BE OUTSIDE THE 0.2'1:
ANNUAL CHANCE FLOOD PLAIN
GENERAL PLAN LAND USE DESIGNATION:
EXISTING:
PROPOSED:
SITE: VACANT
NORTH: RESIDENTIAL
SOUTH: VACANT, RESIDENTIAL
NORTHWEST: RESIDENTIAL
SOUTHWEST: VACANT
EAST: RESIDENTIAL, CIVIC, COMMERCIAL
LOTS 1,2,3,5,6: RESIDENTAL
LOT 7: COMMERCIAL
LOTS 4 AND 8: PARK / OPEN SPACE
ZONING DESIGNATION:
EXISTING: SITE:
NORTH:
SOUTH:
NORTHWEST:
SOUTHWEST:
EAST:
DC-DOWNTOWN CENTER
DC-DOWNTOWN CENTER
DC-DOWNTOWN CENTER
DC-DOWNTOWN CENTER
DC-DOWNTOWN CENTER
DC-DOWNTOWN CENTER
PROPOSED:
APN:
SITE: SPECIFIC PLAN 222 OVERLAY, TO BE ADDED
TO DC-DOWNTOWN CENTER
487-470-031 & 487-470-030
PROJECT AREA:
GROSS: 63.50 ACRES
NET: 57.34 ACRES
•INCLUDES AREAS OF EXISING PARCELS (PRIOR TO BAY VACATION) AS GROSS, MINUS ONSITE RIGHT OF WAY EASEMENTS FOR NET.
EARTHWORK:
95,92,378 CY CUT
82,480 CY FILL
9 898 CY SHRINKAGE
0 CY IMPORT /EXPORT (BALANCE)
LOT AREAS
EXISTING EXISTING DEDICATION/
PROPERTY LINE
RIGHT-OF-WAY
EASEMENT/SETBACK
STREET CENTERLINE
CURB
CURB & GUTTER
WATER MAIN
SANITARY SEWER LINE
STORM DRAIN LINE
GAS LINE
EDISON
TELEPHONE
OIL
CITY OF MORENO VALLEY
TV
ACRE
SQUARE FEET
CENTERLINE
CURB
EXISTING
FLOW LINE
MEDIAN
OPEN SPACE
PUBLIC FACILITY
PRIVATE ACCESS EASEMENT
PROPERTY LINE
RIGHT OF WAY
STORM DRAIN
SANITARY SEWER
TOP OF CURB
TOP OF GRATE
BOTTOM OF WALL
TOP OF WALL
UNLESS NOTED OTHERWISE
NOT A PART OF THIS PLAN
EXISTING PROPOSED
---X"V,v-/ ---
---x·s---
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AC
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PL / 11,
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SD
ss
TC
TG
BW
TW
U.N.O.
NAP
CITY PEN NUMBERS:
(PEN22-0077)
THOMAS BROS PAGE:
PAGE:
PAGE:
PAGE:
PAGE:
COMMENTS
718, GRID: A4
718, GRID: AS
718, GRID: 84
718, GRID: 85
OWNER:
CITY MORENO VALLEY
LOT R/W OR EASEMENT SUBDIVISION (AC)
14177 FREDERICK ST.,
MORENO VALLEY, CA 92553
LOT
COTTONWOOD AVENUE D 0.61 0.0610
NASON STREET E 1.4340 2.3190
ALLESANDRO AVENUE F 1.6620 0.1100
BAY AVENUE A 2.4260
"A" STREET B,C
EMl'lll 0.251'
LOT 1 1 26.2920
LOT 2 2 34.4600
LOT 3 3
LOT 4 4
LOT 5 5
LOT 6 6
LOT 7 7
LOT 8 8
SUM AREAS 66.8830 2.7410
TOTAL AREAS
69.624 AC
(EX)
0.7080 (RE)DEDICA TE
3.9390 (RE)DEDICA TE
1.9070 (RE)DEDICA TE
1.8460 VACATE, REDEDICATE
3.8880 DEDICATE
MAINTAIN
6.9220 RESIDENTIAL
8.5960 RESIDENTIAL
5.7460 RESIDENTIAL
3.4980 OPEN SPACE
7.4480 RESIDENTIAL
7.7430 RESIDENTIAL
16.0060 COMt.tERICAL
1.3770 OPEN SPACE
69.6240
69.624 AC. (PR)
DEVELOPER:
LEWIS MANAGEMENT CORP.
ATTENTION: JOSEPH EDWARDS
1156 NORTH MOUNTAIN AVENUE
UPLAND, CALIFORNIA 91785-0670
PHONE: (909) 985-0971
EN GI NEER /SURVEYOR:
CANNON
ATTENTION: WILHELM MAUL
16842 VON KARMAN AVENUE, SUITE 150
IRVINE, CA, 92606
PHONE: 949-668-1683
UTILITIES:
-----------
'-... , WATER:
SEWER:
GAS:
EASTERN MUNICIPAL WATER DIS , ICT
EASTERN MUNICIPAL WATER DISTl!IICT
SOUTHERN CALIFORNIA GAS COMP.ANY
ELECTRIC:
TELECOMMUNICATIONS:
CITY OF MORENO VALLEY
FRONTIER & SPECTRUM
OWNER STATEMENT: ',, THE OWNER, AS IDENTIFIED HEREIN, IS FEE OWNER OF THE EXISTING LOTS NORTH AND SOUTH OF THE EXISTING -,,r------ BAY AVENUE AT THE TIME OF THE TENTATIVE MAP '-,,_ PREPARATION. --,,_ i ,_, "\.,..., ',,
PORTIONS OF BAY, ALESSANDRO, AND NASON THAT ABUT THE PROJECT EXIST AS RIGHT OF WAY AND WILL PROJECT DESCRIPTION '-,,,, './6: 1602~ ' ::::c-~ EASEMENT \ Oo ., ........ \ TABLE8E RE-DEDICATED AS PART OF THE MAP
AFFECTS PURPOSE REFERENCE BENEFICIARY DOC/LOC
EXISTING
1 PUBUC UTILITIES & DOC #1977-43349 OF SCEC
INCIDENTAL PURPOSE OFFICIAL RECORDS
2 BOUNDARY BOOK 80, PAGE 53 OF COUNTY OF
RECORDS OF SURVEY RIVERSIDE
3 ROAD & UTILITIES DOC #1993-211297 OF CITY OF MORENO
OFFICIAL RECORDS VALLEY
4 PIPELINE DOC #2012-0177957 OF EMWD
OFFICIAL RECORDS
5 ROAD & UTILITIES DOC #2013-463248 OF CITY OF MORENO
OFFICIAL RECORDS VALLEY
6 DRAINAGEDO DOC #2013-484376 OF CITY OF MORENO
OFFICIAL RECORDS VALLEY
PROPOSED
AA DRAINAGE EASEMENT DEDICATED WITH MAP
BB MUV ELECTRIC DEDICATED PER
SEPARATE DOCUMENT
cc EMl'lll DEDICATED PER
SEPARATE DOCUMENT
PR. COMMENT DISPOSITION
QUITCLAIM
QUITCLAIM
CONVERT TO
RIGHT OF WAY
QUITCLAIM
CONVERT TO
RIGHT OF WAY
MAINTAIN
PROPOSED
PROPOSED
PROPOSED
-- ~E ~~oii~~N~s ~~o~~~~E l~~l~E~~~R6~~ oN-,\____ ■- \\1t]"--?i"k-----', ...... , \.,,_ __ , ,.., LIMITS, SUBDIVISION OF THE RESULTING VACATION ljND '-,, , '-----, ADJACENT TWO LOTS TO 6 BUILDABLE PARCELS, ",' \__ 1600-"'-,,· ::;::-----'-_-_" PARK PARCELS, DEDICATION OF BAY AVENUE (TO , t--:::~ \ ',, DEMINSION SHOWN), DEDICATION OF "A" STREET ( 1 ~:;__J '",,, •--_, DIMENSION SHOWN), REDEDICATION AND CONVERSI ) OF -,,,,_- , ',,,--,_,, RIGHT OF WAY EASEMENTS FOR ADJACENT COTTO 000--,, 0 ·-''-'11"'-' ;:: , _~, +----'',_,__ -, __ ,,,- AVENUE, ALESSANDRO AVENUE, AND NASON STR T. \ _ gJ...J ' 1598__;:, THE PROJECT DOES NOT PROPOSE LOT-SPECIF\C --_ _ _, ,, fTifr6i----- :~~~E~ ~;RRENT WITH MAPPING. 'i, '',--,,,,, = ',,_''-,,,,,~~:~~T :cf----",_,---,_,~~.9-~..,.,.,..., ' ' THERE ARE NO WELLS WITHIN THE PROJECT OR
200' OF THE PROJECT '-,-, 1595..2i..=-=':-' ' '== ""C'.,--,,A,,,__ -,_,_ ....... , -- .. _ _, ~;~ ~f ;~~\;~~~~P!osrn sTRucwnl e l-S,:-__ -_-__ -_-__ -_ -- ~\,,_ ·Hll·~=-...,,;;~·-: =1:J:s:;9:;-4;=_ '=,,:_t==_-,._--=--::::,--,_-,-__ -_-__ -,-__ -Cz-_ 7 -,_-,-_-,,-,_-,_---'
THERE ARE NO EXISTING OR PROPOSED WA
THE PROJECT SITE.
LANDSCAPE NOTE
, .
',,,, __ ~ .......... _ ... ____ L28 115S
> LANDSCAPING WITHIN THE ROUNDABOUT, MEDIANS OR
PROPOSED PARKS MAY BE MAINTAINED BY THI,\_ JY
THORUGH A COMMUNITY FACILITY DISTRICT (CFO). '!.-OJ:&.
A AND B (PARK LOTS) TO BE INCORPORATED IN ""'i1-IE '---,, •- ,_,- CFO FOLLOWING APPROVAL OF LOT-SPECIFIC PLA S '-,,__ ./
(SEPARATE GRADING/DEVELOPMENT PLAN, WQM_P) •- ,_,
- -L20_
NO. Ii 38421
' 111
----+
' '
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' _,.
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SURVEY NOTE
2 3
4 5
6 7
8 9
10 11
PRELIMINARY GRADING PLAN
PRELIMINARY GRADING PLAN
PRELIMINARY GRADING PLAN
PRELIMINARY GRADING PLAN
PRELIMINARY GRADING PLAN
PRELIMINARY GRADING PLAN
PRELIMINARY GRADING PLAN
OFFSITE SITE PLAN
BOUNDARY SECTIONS
ROAD CROSS SECTIONS
CONCEPT UTILITY PLAN
Parcel
Line #/Curve #
C1
C2
C3
C4
C5
C6
C7
CB
C9
C10
C14
C15
C16
C17
C18
C19
C20
C21
C22
C23
C24
C25
C26
C27
C28
L1
L2
L3
L4
L5
L6
L7
LB
L9
L10
L11
L12
L13
L14
MORENO VALLEY FRWY.
BAY AV.
60 SITE
a::
BAY AV. c::,
h! r-----;----
"1
~ -
cs
ALLESSANDRO BLVD.
Line and Curve
Table
Length Bearing/Delta
60.43' 20.73
84.31' 20.73
25.49' 58.42
40.39' 26.91
25.52' 58.50
60.42' 20.73
2.65' 0.65
25.52' 58.50
40.65' 27.08
25.56' 58.58
204.76' 5.92
53.38' 5.92
25.52' 58.50
40.41' 26.92
25.49' 58.42
25.56' 58.58
40.63' 27.07
13.27' 30.42
12.25' 28.08
81 .56' 20.06
58.46' 20.06
40.95' 20.06
58.67' 20.13
81.85' 20.13
99.42' 20.13
367.00 N0"25'56"E
104.82 S89'34'04"E
150.00 N0"25'56"E
33.96 N46'57'5B"W
489.33 S89'33'23"E
33.99 S46'57'52"E
512.95 s0·25'53"w
594.20 S89'56' 4B"E
137.28 S21"09'53"W
375.39 S0"26'03"W
458.16 N 89"33' 38"W
702.95 N0"25'56"E
578.19 S89"33'27"E
390.92 s0·25•5o•w
CACTUS AV.
Radius
167.00'
233.00'
25.00'
86.00'
25.00'
167.00'
233.00'
25.00'
86.00'
25.00'
1983.00'
517.00'
25.00'
86.00'
25.00'
25.00'
86.00'
25.00'
25.00'
233.00'
167.00'
117.00'
167.00'
233.00'
283.00'
MAP
NOT TO SCALE
Parcel Line and Curve
Table
Line #/Curve # Length Bearing/Delta Radius
L15 652. 71 NB9"33' 40"W
L16 200.95 N0'26'01"E
L17 137.28 N21'09'53"E
L1B 212.00 s0·25•5o•w
L19 31.24 S40"14'39"W
L20 570.94 NB9'33'38"W
L21 174.27 N0'26'01 "E
L22 627.06 N0"26'22"E
L25 519. 73 NB9'33' 4B"W
L27 0.21 S45'26'02"W
L28 496. 79 NB9'33'57"W
L29 593.06 N0'26'21 "E
L31 31.25 S39'23'41"E
L32 104.88 s0·25'5o•w
L33 300.1 o so·os· 32"E
L34 186.30 s0·25'5o•w
L35 35. 75 S6"20' 4B"W
L36 2s1.51 s0·25•5o•w
L37 29.21 S38"28' 45"W
L38 271.02 NB9'33'57"W
L39 70.35 S84'43'25"W
L40 144. 72 N89'33'57"W
L41 715.00 N0"26'01"E
L42 458.15 NB9'33'38"W
L43 570.94 S89'33'38"E
L44 565.48 N0"26'01 "E
L45 656.23 N0"26'01 "E
L46 90.91 N0'26'01 "E
L47 177.99 N19'37'20"W
L48 177.99 N19'37'20"W
L49 177.99 N19'37'20"W
L50 174.40 N0"30'22"E
L51 174.40 N0"30'22"E
L52 197.19 N0'30'22"E
L53 84. 77 S89"29'38"E
L54 32.53 N45'30'22"E
L55 32.53 N44'29'38"W
L56 27.00 NB9'29'38"W
~" l------------------------..---------------------------,-------------------,:-:--:::=-::::::-::----------r:::-::---===--==---------~----------------------7r;.;AT;:c=:E•.:---7 7'6'/;;,2;,-2----J ~ GEOTECHNICAL REVIEW I HEREBY CERTIFY THAT: PLAN PREPARED BY: PLAN PREPARED FOR:
e THIS PLAN HAS BEEN REVIEWED AND CONFORMS TO RECOMMENDATIONS 1. THESE PL.ANS HAVE BEEN PREPARED UNDER MY JOB NO. 211203 '
a. SUPERVISION:
OF THE SOILS ENGINEERING/GEOLOGIC REPORT DATED ----- 2. THE GRADING SHOWN HEREON WILL NOT DIVERT DRAINAGE CPN: PEN22-077 FROM ITS NATURAL DOWNSTREAM COURSE OR OBSTRUCT ~ TTM: 36421 THE DRAINAGE OF ADJACENT PROPERTIES: " Cannon LEw1s MANAGEMENT coRP. SHEET _3 1156 NORTH MOUNTAIN AVENUE
N UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY
0 TEL: (909) 985-0971 1 1 1 < PREPARED BY: CALIFORNIA o ENGINEER 8/1/2022 8/1/2022 f L _____________________________ .l._ _____ -_-_-:w~""l:.::L""'H~-=E=...,L=M-=-"""=J-._...,.M::::...,A=...,u=-L---_-_-_-_-_-_-_-_ ..:E::_X~P._::DA~T~E ____ _:~======~--.1..AAA~~O~N~P~--T~IL:'.L~M~AN~N:'..:S~----=EX:::P..:.·...:D=A::.TE:_ ________ ..1.. ____ _::...._ _________ ..1.. ________________ L ____________________________ _j_ __ _:o:.:.F __ _J
SIGN DATE
<
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
PRELIMINARY GRADING PLAN
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1. THESE PLANS HAVE BEEN PREPARED UNDER MY
SUPERVISION:
2. THE GRADING SHOWN HEREON WILL NOT DIVERT DRAINAGE
FROM ITS NATURAL DOWNSTREAM COURSE OR OBSTRUCT
THE DRAINAGE OF ADJACENT PROPERTIES:
1,,/ ,,
WATER MAIN
SANITARY SEWER LINE
STORt.4 DRAIN LINE
EASEMENT. SEE SHEET 1
SWALE LINEWORK.
EXISTING
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1 PUBLIC UTILITIES &
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3 ROAD & UTILITIES
4 PIPELINE
PROPOSED
AA DRAINAGE EASEMENT
BB MUV ELECTRIC
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Parcel Line and Curve
Table
Line #/Curve # Length Bearing/Delta Radius
C1 60.43' 20.73 167.00'
C2 84.31' 20.73 233.00'
C6 60.42' 20.73 167.00'
C7 2.65' 0.65 233.00'
L1 367.00 N0'25'56"E
L2 104.82 S89"34'04"E
L3 150.00 N0'25'56"E
L4 33.96 N46'57'58"W
L5 489.33 S89'33'23"E
L6 33.99 S46'57'52"E
L7 512.95 S0'25'53"W
LB 594.20 S89'56'48"E
L9 137.28 S21 '09'53"W
L17 137.28 N21 '09'53"E
REFERENCE BENEFICIARY PR. COMMENT DOC/LOG DISPOSITION
DOC #1977-43349 OF SCEC QUITCLAIM
OFFICIAL RECORDS
DOC #1993-211297 OF CITY OF MORENO CONVERT TO
OFFICIAL RECORDS VALLEY RIGHT OF WAY
DOC #2012-0177957 OF EMWD MAINTAIN
OFFICIAL RECORDS
DEDICATED ~TH MAP
DEDICATED PER
SEPARATE DOCUMENT
DEDICATED PER
SEPARATE DOCUMENT
PROPOSED
PROPOSED
PROPOSED
CONSTR.UCTION ~01:BS
(i)
®
0 0
0 ©
0 @
11 PROPOSED STORM DRAIN
PROPOSED EMWD WATER MAIN
PROPOSED EMWD SEWER MAIN
PROPOSED INLET
PROPOSED SEDIMENTATION BASIN
PROPOSED CURB
PROPOSED SIDEWALK
PROPOSED EDGE OF PAVEMENT
PROPOSED DRAINAGE SWALE
COITONWOOD ~
1//'
BA.Y A\$NUE
3 5
----1
KEY MAP 0
1" = BOO'
DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 3B421
SHEET _3 SIGNATURE DATE ROAD PAVEMENT 1156 NORTH MOUNTAIN AVENUE N _D_ UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY 0 INLET Ii] 1ZI:JS1 TEL: (909) 985-0971 2 1 1 < PREPARED BY: CALIFORNIA o ENGINEER 8/1/2022 3' ---,W""l""L,.,H"'ELc:-M.,-,J,--. ""'M-cAccU-,.,L_____ EXP. DATE STORMWA TER BMP SEDIMENT TRAP OF ,;: L_ _______________ l_ __ __::_:_:::.:.==_..:::....::::::.::..=...._ __ ___::::....:....::::.'...:.__ __ ~~=--_J_ ______ ~ ~~~--..L_---==------_J_--------_l_---------------L_______::_ _ _J <
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
PRELIMINARY GRADING PLAN
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DATE: 7 /6/22
JOB NO. 211203
f Cannon LEWIS MANAGEMENT CORP.
CPN: PEN22-077
TTM: 38421
SHEET _ SWALE LINEWORK.
;:J- SIGNATURE DATE ROAD PAVEMENT 1156 NORTH MOUNTAIN AVENUE N 0 __o_ UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY INLET Iii] IZDSI < PREP'REO BY:
TEL: (909) 985-0971 3 1 1
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.;:L__ _____________ _j_ __ ~~::...::::::~--~~---=~~-L__-----~ ~ ~ --_.l_--='__ ___ _JL__ ______ __J_ _____________ _____L-=-_::____J <
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DOC #2013-463248 OF
OFFICIAL RECORDS
DEDICATED W11H MAP
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3 //
--------------l 1 KEY MAP 0
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DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 38421
;:J- SIGNATURE DATE
SHEET
ROAD PAVEMENT 1156 NORTH MOUNTAIN AVENUE N
0 __o_ UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY INLET Iii] IZDSI < PREP'RED BY:
TEL: (909) 985-0971 4 1 1
CALIFORNIA o " ~ ENGINEER __________ 8/1/2022 J, WILHELM STORMWAlER BMP SEDIMENT TRAP J. MAUL EXP. DATE OF
.;:L_ _____________ _j__ __ ~~::...::::::~--~~---=~~-L_-----~ ~ ~ --_.l_---='__ ___ _JL__ ______ __J_ _____________ ______L _ _::_____J <
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NO. 42549
WILHELM JOHN MAUL
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E
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STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
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REFERENCE
DOC/LOC
C14
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L34
L35
L36
L37
L38
L39
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BOOK 80, PAGE 53 OF
RECORDS OF SURVEY
DOC #1993-211297 OF
OFFICIAL RECORDS
DOC #2013-463248 OF
OFFICIAL RECORDS
DOC #2013-484376 OF
OFFICIAL RECORDS
DEDICA TIED WITIH MAP
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SEPARATIE DOCUMENT
DEDICA TIED PER
SEPARATIE DOCUMENT
204.76'
53.38'
40.95'
81.85'
99.42'
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35.75 281.51
29.21 271.02
70.35 144.72
177.99
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BENEFICIARY
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RIVERSIDE
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CllY OF MORENO
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CllY OF MORENO
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5.92 1983.00'
5.92 517.00'
20.06 117.00'
20.13 233.00'
20.13 283.00'
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PR.
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QUITCLAIM
CONVERT TO
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CONVERT TO
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VACATIE
PROPOSED
PROPOSED
PROPOSED
CON811llJCl10N NOIES
0 PROPOSED EMWIJ WATER MAIN
0 PROPOSED EMWIJ SEWER MAIN
0 PROPOSED INLET
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0 PROPOSED SIGNALIZED INTERSECTION
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ALESSANDRO BO,uJ.d>Y.~
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KEY MAP 0 1
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DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 3B421
SHEET
N _O_ UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY o INLET Ii] 1ZI:JS1 TEL: (909) 985-D971
< PREPARED BY: ENGINEER 8/1/2022 CALIFORNIA 5 1 1 J --W-I-LH_E_L_M_J ___ M_A_U_L_____ EXP. DATE STORMWATER BMP SEDIMENT TRAP OF ,;:L _________________________ _L _____ ::.:..:::,:.::.:::::_:_:_::::_:.=..::._ _____ .::::_..:__::..:. ____ ~:"=::==::~-__1 ___________ ~ ~~~~ ----_1._ ___ __::=-________ _L _____________ _..l _________________________ l__-=_:::'..'.:.___:,___J <
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
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E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
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SD
@ f Cannon -
LEWIS MANAGEMENT CORP.
SWALE LINEWORK.
Parcel Line and Curve
Table
Line #/Curve # Length Bearing/Delta Radius
cs 25.52' 58.50 25.00'
C9 40.65' 27.08 86.00'
C10 25.56' 58.58 25.00'
C22 12.25' 28.08 25.00'
L14 390.92 s0·25'5o•w
L15 652.71 Ns9·33' 4o•w
L 18 212.00 S0"25'50"W
L19 31 .24 s40·14'39"w
L20 570.94 N89"33'38"W
L31 31.25 S39"23' 41 "E
L32 104.88 s0·25•5o"w
L33 300.10 so·os•32•E
L41 715.00 N0"26'01"E
L43 570.94 S89"33'38"E
REFERENCE BENEFICIARY PR. COMMENT DOC/LDC DISPOSITION
DOC #1977-43349 OF SCEC QUITCLAIM
OFFICIAL RECORDS
DOC #1993-211297 OF CITY OF MORENO CONVERT TO
OFFICIAL RECORDS VALLEY RIGHT OF WAY
DOC #2013-463248 OF CITY OF t.40RENO CONVERT TO
OFFICIAL RECORDS VALLEY RIGHT OF WAY
DEDICATED W11H MAP PROPOSED
DEDICATED PER PROPOSED
SEPARATE DOCUMENT
DEDICATED PER PROPOSED
SEPARATE DOCUMENT
CONSJ'RUCI'ION NOTFS
0 PROPOSED EMWD WATER MAIN
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COITONWOOD A+
2 <t> ~
M.YA~
3 --------------l 1 KEY MAP 0
1" - 800'
DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 38421
SHEET
Iii ~
;:J- SIGNATURE DATE ROAD PAVEMENT 1156 NORTH MOUNTAIN AVENUE N UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY 0 INLET < PREP'RED BY:
TEL: (909) 985-0971 6 1 1
CALIFORNIA
o " ~ ENGINEER 8/1/2022 J, WILHELM STORMWATER BMP SEDIMENT TRAP J. MAUL EXP. DATE OF
.;:L_ _____________ _j_ __ ~~::...::::::~--~~---=~~-L_-----~~~--_l___----='____ ___ _JL_ ______ _____J_ _____________ _____L_::__::____J <
16842 Von Karman Avenue, Suite #150
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949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
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Parcel Line and Curve
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C1 60.43' 20.73 167.00'
C6 60.42' 20.73 167.00'
C7 2.65' 0.65 233.00'
L7 512.95 s0·25•53"w
L13 578.19 S89"33'27"E
L14 390.92 s0·25•5o•w
L17 137.28 N21 "09'53"E
REFERENCE BENEFICIARY PR. COMMENT DOC/LOC DISPOSITION
DOC #1993-211297 OF Cl1Y OF MORENO CONVERT TO
OFFICIAL RECORDS VALLEY RIGHT OF WAY
DEDICATED PER PROPOSED
SEPARATE DOCUMENT
DEDICATED PER PROPOSED
SEPARATE DOCUMENT
CONSTR.lJCl10N Jt-tOIES
0 PROPOSED STORM DRAIN
0 PROPOSED EM\\O WATER MAIN
0 PROPOSED EM\\O SEWER MAIN
0 PROPOSED INLET
© PROPOSED CURB
0 PROPOSED SIDEWALK
COITONWOOD A+
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ALESSANDRO eoUARD
5 ----1
KEY MAP 0
,· = 800'
DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 3B421
SHEET _3 SIGNATURE DATE ROAD PAVEMENT 1156 NORTH MOUNTAIN AVENUE N __D__ UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY 0 INLET Ii] 1ZI:JS1 TEL: (909) 985-0971 7 1 1 < PREPARED BY: CALIFORNIA o ENGINEER 8/1/2022 3' -----,W"'lc-L,-,H"'EL""Mc-,,-J,-_ ""'M..,.A,.,U""L_____ EXP. DATE STORMWA TER BMP SEDIMENT TRAP OF c;: L_ _______________ l_ __ ____::_:_:==...:::....:::::=-=----__ __::::....:....::::.'...:___ __ ~~=---_L ______ ~ ~~~--..L_---=:___ ____ _j__ ________ __J_ _______________ L_____::_ _ _J <
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
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1. THESE PLANS HAVE BEEN PREPARED UNDER MY
SUPERVISION:
2. THE GRADING SHOWN HEREON WILL NOT DIVERT DRAINAGE
FROM ITS NATURAL DOWNSTREAM COURSE OR OBSTRUCT
THE DRAINAGE or ADJACENT PROPERTIES:
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0 PROPOSED EMWD SEWER MAIN
0 PROPOSED INLET
0 PROPOSED SEDIMENTATION BASIN
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0 PROPOSED MEDIAN LANDSCAPING
© PROPOSED SIGNALIZED INlERSECTION
0 PROPOSED SIDEWALK
@ PROPOSED EDGE OF PAVEMENT
SHEET 2
--------------1 1 KEY MAP 0
1· - 800'
DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 38421
;:J- SIGNATURE DATE
SHEET
ROAD PAVEMENT 1156 NORTH MOUNTAIN AVENUE N
0 _a_ UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY INLET Iii] IZDSI < PREP'REO BY:
TEL: (909) 985-0971 8 1 1
CALIFORNIA o " ~ ENGINEER __________ 8/1/2022 J, WILHELM STORMWAlER BMP SEDIMENT TRAP J. MAUL EXP. DATE OF
,;:L_ _____________ _j_ __ ~~::...::::::~--~~---=~~-L_-----~ ~ ~ --_l__---='__ ___ _JL_ ______ __J_ _____________ __L-=-_::____J 16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
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:;:;1-------------------------------,,---------------------------------, g GEOTECHNICAL REVIEW "O
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"- THIS PLAN HAS BEEN REVIEWED AND CONFORMS TO RECOMMENDATIONS or THE SOILS ENGINEERING/GEOLOGIC REPORT DATED -----
I HEREBY CERTIFY THAT:
1. THESE PLANS HAVE BEEN PREPARED UNDER MY
SUPERVISION:
PLAN PREPARED BY:
ALLESSANDRO
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1610
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2. THE GRADING SHOWN HEREON WILL NOT DIVERT DRAINAGE
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THE DRAINAGE or ADJACENT PROPERTIES: f Cannon LEWIS MANAGEMENT CORP. ~ SIGNATURE DATE ~ 1156 NORTH MOUNTAIN AVENUE 0+50
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KEY MAP
DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 3B421
SHEET
N UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY
<-'.; ~ PREPARED BY: TEL: (909) 985-D971 9 1 1
o ENGINEER 8/1/2022 CALIFORNIA 3' --W-1-LH_E_L_M_J ___ M_A_U_L____ EXP. DATE OF s:L _________________________ _L _____ ::.:..:::.:.::.:::::.....:..:....::::.:.=..::._ _____ .::::_.:....:.:..:. ____ ~:"=::==::~-__1 ____________________ __1_ ___ _::=-________ __L _____________ _..l _________________________ l_-=___:::'..'.:__.:___J 16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
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THIS PLAN HAS BEEN REVIEWED AND CONFORMS TO RECOMMENDATIONS or THE SOILS ENGINEERING/GEOLOGIC REPORT DATED -----
DATE
I HEREBY CERTIFY THAT:
1. THESE PLANS HAVE BEEN PREPARED UNDER MY
SUPERVISION:
2. THE GRADING SHOWN HEREON WILL NOT DIVERT DRAINAGE
FROM ITS NATURAL DOWNSTREAM COURSE OR OBSTRUCT
THE DRAINAGE or ADJACENT PROPERTIES:
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PLAN PREPARED FOR:
f Cannon LEWIS MANAGEMENT CORP.
12· 8"
11'
6.5'
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MAX
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PROPOSED
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6.5'
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~ SIGNATURE ~ 1156 NORTH MOUNTAIN AVENUE
2'
MIN.
2:1
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MAX
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TTM 38421
DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 3B421
SHEET
N UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY
<-'.; ~ PREPARED BY: TEL: (909) 985-0971 0 1 1
o ENGINEER 8/1/2022 CALIFORNIA
3' --W-IL_H_E-LM_J ___ M_A_U_L_____ EXP. DATE OF s:L _________________________ _L _____ ::.:..:::_:.::.:::::.....:..:....::::.:.=..::._ _____ .::::..:....:.:..:. ____ ~:"=::==::~-_1 ____________________ _1_ ___ __::=-________ _L _____________ _..l _________________________ l..:..._=::'..'.:__.:..__J
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A STREET
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TOWN CENTER AT MORENO VALLEY
TENTATIVE TRACT MAP 38421
CONCEPT UTILITY PLAN
16842 Von Karman Avenue, Suite #150
Irvine, CA 92606
949.668.1683
NO. 42549
WILHELM JOHN MAUL
R
E
GISTERED PROFESSIONAL ENGIN
E
E
R
STATE OF CALIFORNIA
EXP.
CIV IL
03/31/2024
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THIS PLAN HAS BEEN REVIEWED AND CONFORMS TO RECOMMENDATIONS OF THE SOILS ENGINEERING/GEOLOGIC REPORT DATED ___ _
I HEREBY CERTIFY THAT:
1. THESE PLAHS HAVE BEEN PREPARED UNDER MY
SUPERVISION:
2. THE GRADING SHOWN HEREON WILL NOT DIVERT DRAINAGE
FROM ITS NATURAL DOWNSTREAM COURSE OR OBSTRUCT
THE DRAINAGE OF ADJACENT PROPERTIES:
WATER MAIN
SANITARY SEWER LINE
STORM DRAIN LINE
EASEMENT. SEE SHEET 1
SWALE LINEWORK.
EXISTING
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CONSI'Rl.JCIION NO'IES
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0 PROPOSED EMWD SEWER MAIN
0 PROPOSED INLET
© PROPOSED CURB
0 PROPOSED MEDIAN LANDSCAPING
0 PROPOSED SIDEWALK
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1 INCH = 100 FEET
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DATE: 7 /6/22
JOB NO. 211203
CPN: PEN22-077
TTM: 38421
SHEET
SIGNATURE DATE ROAD PAVEMENT 1156 NORTH MOUNTAIN AVENUE N 0 _a_ UPLAND, CALIFORNIA 91785-0670 CITY OF MORENO VALLEY INLET liJ IZDSI
< PREP'REO BY:
TEL: (909) 985-0971 1 1 1 1
CALIFORNIA
o " ~ ENGINEER __________ 8/1/2022 J, WILHELM STORMWAlER BMP SEDIMENT TRAP J. MAUL EXP. DATE OF
.;:L_ _____________ _j_ __ ~~::...::::::~--~~---=~~-L_-----~ ~ ~ --_.l_---='__ ___ _JL__ ______ __J_ _____________ ___l__...::____J - 34 -
Appendix 3: Soils Information
Geotechnical Study and Other Infiltration Testing Data
Draft
GEOTECHNICAL EXPLORATION
MORENO VALLEY TOWN CENTER
NORTHWEST CORNER OF ALESSANDRO BLVD AND
NASON STREET
MORENO VALLEY, CALIFORNIA
Prepared for
LEWIS LAND DEVELOPERS, LLC
1156 North Mountain Avenue
Upland, California 91786
Project No. 13177.002
July 23, 2021
Draft
July 23, 2021
Project No. 13177.002
Lewis Land Developers, LLC
1156 North Mountain Avenue
Upland, California 91786
Attention: Mr. Bill Hoover, Vice President-Development Feasibility Subject: Geotechnical Exploration
Moreno Valley Town Center
Northwest Corner of Alessandro Blvd and Nason Street
Moreno Valley, California
In accordance with your request, we are pleased to present this geotechnical exploration report for the subject project. This report presents our findings, conclusions and recommendations pertaining to the geotechnical aspects of the proposed development.
It is our opinion that the overall site appears suitable for the intended use provided our recommendations included herein are properly incorporated during design and construction phases of development.
If you have any questions regarding this report, please do not hesitate to contact the undersigned. We appreciate this opportunity to be of service on this project.
Respectfully submitted,
LEIGHTON AND ASSOCIATES, INC.
Simon I. Saiid, GE 2641
Principal Engineer
Robert F. Riha, CEG 1921
Sr. VP / Sr. Principal Geologist
Distribution: (1) Addressee (PDF copy)
Draft
Geotechnical Exploration 13177.002
Moreno Valley Town Center, Moreno Valley, California July 23, 2021 - i -
T A B L E O F C O N T E N T S
Section Page
1.1 Purpose and Scope.............................................................................................1
1.2 Site Location and Description .............................................................................1
1.3 Proposed Development.......................................................................................2
2.1 Field Exploration..................................................................................................3
2.2 Laboratory Testing ..............................................................................................3
3.1 Regional Geology................................................................................................4
3.2 Site Specific Geology ..........................................................................................4
3.2.1 Artificial Fill (Stockpile)........................................................................................4
3.2.2 Alluvial Deposits .................................................................................................4
3.3 Landslide/Debris Flow and Rock Fall..................................................................5
3.4 Rippability............................................................................................................5
3.5 Groundwater and Surface Water ........................................................................5
3.6 Faulting................................................................................................................5
3.7 Ground Shaking ..................................................................................................5
3.8 Dynamic Settlement (Liquefaction and Dry Settlement).....................................6
3.9 Expansive Soils...................................................................................................6
3.10 Slope Stability......................................................................................................6
3.11 Percolation/Infiltration Testing.............................................................................7
4.1 General................................................................................................................8
4.2 Earthwork ............................................................................................................8
4.2.1 Site Preparation and Remedial Grading.............................................................8
4.2.2 Suitability of Site Soils for Fills............................................................................9
4.2.3 Shrinkage ...........................................................................................................9
4.2.4 Import Soils.......................................................................................................10
4.2.5 Utility Trenches.................................................................................................10
4.2.6 Drainage...........................................................................................................10
4.2.7 Slope Construction ...........................................................................................10
4.3 Foundation Design ............................................................................................11
4.3.1 Bearing and Lateral Pressures.........................................................................11
4.4 Retaining Walls .................................................................................................12
4.5 Foundation Setback from Slopes......................................................................13
4.6 Sulfate Attack ....................................................................................................14
1.0 INTRODUCTION .................................................................................................... 1
2.0 FIELD EXPLORATION AND LABORATORY TESTING ....................................... 3
3.0 GEOTECHNICAL AND GEOLOGIC FINDINGS .................................................... 4
4.0 CONCLUSIONS AND RECOMMENDATIONS ...................................................... 8 Draft
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4.7 Concrete Flatwork .............................................................................................14
4.8 Preliminary Pavement Design...........................................................................14 Accompanying Tables, Figures, Plates and Appendices
Tables
Table 1. CBC Site-Specific Seismic Coefficients............................................................ 6 Table 2. Summary of Percolation/Infiltration Test Results.............................................. 7 Table 3. Conventional Foundation Requirements ........................................................ 12 Table 4. Retaining Wall Design Earth Pressures (Static, Drained)............................... 12 Table 5. Footing Setbacks............................................................................................ 13 Table 6. Asphalt Pavement Sections............................................................................ 14 Figures
Figure 1 – Site Location Map Rear of Text
Figure 2 – Boring Location Plan Rear of Text
Figure 3 – Regional Geology Map Rear of Text
Figure 4 – Liquefaction Hazard Map Rear of Text
Appendices
Appendix A – Field Exploration / Logs of Borings
Appendix B – Geotechnical Laboratory Test Results
Appendix C – Earthwork and Grading Specifications
Appendix D – GBA Important Information About This Geotechnical Engineering Report
5.0 GEOTECHNICAL CONSTRUCTION SERVICES ................................................ 16
6.0 LIMITATIONS ....................................................................................................... 17 REFERENCES .............................................................................................................. 18 Draft
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I N T R O D U C T I O N
1.1 Purpose and Scope
This geotechnical exploration report is for the Moreno Valley Town Center residential project located at the Northwest Corner of Alessandro Blvd and Nason Street, in Moreno Valley, California (see Figure 1). Our scope of services for this geotechnical exploration included the following:
Review of available site-specific reports and published data, including various geologic publications listed in the references at the end of this report. A review of the provided site plan.
Site reconnaissance and visual observations of surface conditions to evaluate any potential localized settlement or other surface distresses. Excavation of eight (8) geotechnical borings and four (4) percolation-infiltration tests to explore the subsurface soil conditions within the site. Approximate locations of these explorations are depicted on Figure 2. The logs of borings and percolation tests are included in Appendix A.
Laboratory testing was performed on representative samples and results are included in Appendix B.
Geotechnical engineering analyses performed or as directed by a California registered Geotechnical Engineer (GE). A California Certified Engineering Geologist (CEG) performed engineering geology review of site geologic hazards. Preparation of this update report, which presents the results of our geotechnical exploration and preliminary recommendation for site development.
This report is not intended to be used as an environmental assessment (Phase I or other), and foundation and/or a rough grading plan review.
1.2 Site Location and Description
Based on information provided, the approximately 59-acre site is tentatively planned to be developed into a mixed residential (37 acres in the north) and non-residential (16 acres in the south), with a park and library (in the center portion). The overall property consists of the following APNs: 487-470-030 (21.94 acres), 487-470-031 (34.48 acres), and future Bay Ave ROW vacated (2.19 acres). The site is currently undeveloped with a large stockpile of fill in the southeastern corner. Small vegetation growth including weeds and seasonal grasses cover most of the site. The site topography slopes gently into southwesterly direction. Site elevations vary from approximately 1590 feet MSL (Mean Sea Level) in the
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southwest corner to a maximum elevation of approximately 1640 feet MSL in the northeast corner of the site.
1.3 Proposed Development
No specific plans were provided to our office regarding proposed site development.
However, based on personal communications, we understand that the residential development will host typical one- or two-story single-family residential homes consisting of wood-frame structures with conventional slab-on-grade foundations. The foundation loads are not expected to exceed 2,500 pounds per lineal foot (plf) for continuous footings.
We also expect the loading and foundation requirements for the non-residential portion of the site to be substantially similar. We anticipate site grading will require maximum cuts and fills on the order of ±10 feet. If site development differs significantly from the assumptions stated herein, our recommendations should be subject to further reviews and evaluations.
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F I E L D E X P L O R A T I O N A N D L A B O R A T O R Y
T E S T I N G
2.1 Field Exploration
Our field exploration consisted of the excavation of eight (8) borings and four (4) percolation/infiltration tests within accessible areas of the site. During excavation, bulk samples and relatively “undisturbed” Ring samples were collected from the exploration borings for further laboratory testing and evaluation. Approximate locations of the borings and percolation/infiltration tests are depicted on the Boring Location Plan (Figure 2).
Sampling was conducted by a staff engineer from our firm. After logging and sampling, the excavations were loosely backfilled with spoils generated during excavation.
The exploration logs included within Appendix A and related information depicts subsurface conditions only at the locations indicated and at the particular date designated on the logs. Subsurface conditions at other locations may differ from conditions occurring at these borings locations. The passage of time may result in altered subsurface conditions due to environmental changes. In addition, any stratification lines on the logs represent the approximate boundary between soil types and the transition may be gradual.
2.2 Laboratory Testing
Laboratory tests were performed on representative bulk samples to provide a basis for development of remedial earthwork and geotechnical design parameters. Selected samples were tested to determine the following parameters: maximum dry density and optimum moisture, expansion index, soluble sulfate content, gradation and collapse potential. The results of our laboratory testing are presented in Appendix B.
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G E O T E C H N I C A L A N D G E O L O G I C F I N D I N G S
3.1 Regional Geology
The site is located within a prominent natural geomorphic province in southwestern California known as the Peninsular Ranges. It is characterized by steep, elongated ranges and valleys that trend northwestward. More specifically, the site is situated within the Perris Block, an eroded mass of Cretaceous and older crystalline rock.
The Perris Block, approximately 20 miles by 50 miles in extent, is bounded by the San Jacinto Fault Zone to the northeast, the Elsinore Fault Zone to the southwest, the Cucamonga Fault Zone to the northwest, and the Temecula Basin to the southeast. The southeast boundary of the Perris block is poorly defined. The Perris Block has had a complex tectonic history, apparently undergoing relative vertical land movements of several thousand feet in response to movement on the Elsinore and San Jacinto Fault Zones. Thin sedimentary and volcanic materials locally mantle the crystalline bedrock. Alluvial and colluvial deposits fill the lower valley areas. Based on published geologic maps (see Figure 3), the site is underlain by young and very old fan deposits.
3.2 Site Specific Geology
The geologic units encountered are discussed in the following sections in order of increasing age and further described on the logs of borings in Appendix A.
3.2.1 Artificial Fill (Stockpile)
A large stockpile of artificial fill is located at the southeastern corner of the site.
The source of these materials is not known to us, however the soils appear to substantially similar to the soils explored in the borings. Additionally, artificial fill was encountered in some of our borings in the upper 12 to 24 inches of site soils, which appear to be the result of previous site grading or agricultural activities. The suitability of the stockpile soils to be used as fill materials during grading should be further evaluated during grading.
3.2.2 Alluvial Deposits
The alluvial fan deposits were observed throughout the site to the depths explored of 51 feet below ground surface. As encountered, these soils typically consisted of brown to reddish brown, medium dense to very dense, moist silty sand (SM) and well-graded sand with variable amounts of silt (SW-SM) and interbedded lowplasticity sandy silt (ML) layers. This alluvium is expected to generally possess a very low expansion potential (EI<21). Our laboratory testing indicates the upper 5 to 10 feet of alluvium has a slight to moderate collapse potential (<6%).
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3.3 Landslide/Debris Flow and Rock Fall
No evidence of on-site landslides/debris flow or rock fall was observed during our field investigation and review of referenced reports. Elevated topography and thick deposits of surficial soils typically associated with landsliding or debris flows are not present. Due to the lack of nearby rock outcrop and the gentle natural slope of adjacent hillside areas, the debris flow and rock fall hazard is considered very low.
3.4 Rippability
Based on the results of our geotechnical borings, previous experience in this area, we do not anticipate that bedrock be encountered during site work within the upper 50 feet below ground surface (BGS)
3.5 Groundwater and Surface Water
Groundwater was not encountered during this exploration to the depths explored (51.5 feet). Recent groundwater level was measured in March 2021 at approximately 1470 feet MSL (approximately 40 feet BGS) at well EMWD25695 (339025N1171928W001), which is approximately one-mile south of the site. Thus, we do not anticipate significant groundwater related problems during grading or future development. However, locally perched water conditions can occur and may fluctuate seasonally, depending on rainfall. No surface water was observed.
3.6 Faulting
No indications of faulting or fault related fissuring or fracturing is known to exist or observed onsite. This site is not located within a currently designated Alquist-Priolo Earthquake Fault Zone or County of Riverside Fault Zone.
3.7 Ground Shaking
Strong ground shaking can be expected at the site during moderate to severe earthquakes in this general region. This is common to virtually all of Southern California.
Intensity of ground shaking at a given location depends primarily upon earthquake magnitude, site distance from the source, and site response (soil type) characteristics.
The site-specific seismic coefficients provided in this section are based on an interactive tools/programs currently available on USGS website and OSHPD seismic maps. Based on ASCE 7-16 and our site-specific ground motion analysis for this Class D site, the seismic coefficients for this site are as listed in Table 1 below:
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Table 1. CBC Site-Specific Seismic Coefficients
CBC Categorization/Coefficient Value (g)
Site Longitude (decimal degrees) -117.1940
Site Latitude (decimal degrees) 33.9208
Site Class Definition D
Mapped Spectral Response Acceleration at 0.2s Period, Ss 1.87 Mapped Spectral Response Acceleration at 1s Period, S1 0.74 Short Period Site Coefficient at 0.2s Period, Fa 1.0
Long Period Site Coefficient at 1s Period, Fv 1.7
Adjusted Spectral Response Acceleration at 0.2s Period, SMS 1.87 Adjusted Spectral Response Acceleration at 1s Period, SM1 1.25 Design Spectral Response Acceleration at 0.2s Period, SDS 1.25 Design Spectral Response Acceleration at 1s Period, SD1 0.83 Site-Specific Modified Peak Ground Acceleration, PGAm 0.87 Note: The seismic coefficients for Site Class D follows Exception (2) in Section 11.4.8 of ASCE 7-16 that assumes a fundamental period of vibration less than 0.5s for the proposed structures. The project structural engineer should confirm such assumption or else a site–specific ground motion analysis will be required
3.8 Dynamic Settlement (Liquefaction and Dry Settlement) Ground movements generated during a seismic event can produce settlements in sands or granular earth materials both above and below the water table. The earth materials onsite may experience seismically induced settlement during the design seismic event.
The potential for such seismic densification to manifest at the graded surface and impact the development site is low to moderate.
If remedial grading is performed as recommended, total dynamic densification settlement is estimated to be less than 2 inches globally with anticipated differential settlement of 1- inch in 40 feet.
3.9 Expansive Soils
Limited laboratory testing indicated that near surface soils generally possess a very low expansion potential.
3.10 Slope Stability
It is anticipated that slopes constructed within the site are to be less than 15 feet in height.
If constructed at 2:1 gradient using onsite soils, these slopes should be grossly stable under short- and long-term conditions (including seismic loading).
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3.11 Percolation/Infiltration Testing
Percolation tests and associated test borings were performed in the vicinity of the proposed basins on the center-right and lower-right sections of the site (see Figure 2). Testing was performed in general accordance with the procedures of the Riverside County Flood Control and Water Conservation District (RCFC&WCD) Design Handbook (RCFC, 2011).
The percolation tests (P-1 through P-4) were performed to depths of approximately 5 to 7 feet BGS. Adjacent deeper borings indicate the presence of silty sands to well-graded sands with silts to depths of at least 12 feet BGS. The results of the percolation testing are presented below. A factor of safety has not been applied to these rates.
Table 2. Summary of Percolation/Infiltration Test Results Test
Hole # Location Depth BGS (ft)
Percolation
Rate (min/in)
Infiltration
Rate
(in/hr)
Soil Description
P-1 See Fig 2 7 1.0 2.9 Silty Sand (SM)
P-2 See Fig 2 5 0.7 4.1 Silty Sand (SM)
P-3 See Fig 2 5 1.5 1.5 Silty Sand (SM)
P-4 See Fig 2 5 0.7 3.5 Silty Sand (SM)
I I I I I
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C O N C L U S I O N S A N D R E C O M M E N D A T I O N S
4.1 General
Development of the site appears feasible from a geotechnical viewpoint provided that the following recommendations are incorporated into the design and construction phases of development.
4.2 Earthwork
Earthwork should be performed in accordance with the following recommendations and the Earthwork and Grading Specifications Appendix C. The recommendations contained in Appendix C, are general grading specifications provided for typical grading projects and some of the recommendations may not be strictly applicable to this project. The specific recommendations contained in the text of this report supersede the general recommendations in Appendix C. The contract between the developer and earthwork contractor should be worded such that it is the responsibility of the contractor to place the fill properly in accordance with the recommendations of this report, the specifications in Appendix C, applicable City Grading Ordinances, notwithstanding the testing and observation of the geotechnical consultant.
4.2.1 Site Preparation and Remedial Grading
Prior to grading, the proposed structural improvement areas (i.e. all structural fill areas, pavement areas, buildings, etc.) of the site should be cleared of surface and subsurface obstructions, heavy vegetation, and/or deleterious materials. Roots and debris should be disposed of offsite. Septic tanks or seepage pits, if encountered, should be abandoned in accordance with the County of Riverside Department of Health Services guidelines.
Compressible materials including; undocumented fill, surficial topsoil, and near surface alluvial deposits are potentially compressible in their present state and may settle under the surcharge of fills or foundation loading. As such, these materials should be removed and re-compacted to a minimum of 90 percent relative compaction (based on ASTM D1557). For preliminary planning purposes, the anticipated removal depth is expected to extend to a depth of 6 feet BGS in the northern portion of the site (or north of LB-3), 8 feet in the middle portion of the site (or between LB-4 and LB-5) and 10 feet south of LB-6. The removal limit should be established by a 1:1 (H:V) projection from the edge of fill soils supporting settlement-sensitive structures downward and outward to competent material identified by the geotechnical consultant. Cut slopes exposing alluvial soils greater than 3 feet in height should be removed and replaced as compacted fill slopes in accordance with Appendix C. Removals will also include benching into competent
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material as the fills rise. Areas adjacent to existing structures, property boundary and roadways, may require special monitoring. Temporary cuts in these areas should be no steeper than 1:1 slopes. Deeper removal may be required in localized areas depending on recommendations by the geotechnical consultant.
4.2.2 Suitability of Site Soils for Fills
The onsite soils are generally suitable for re-use as compacted fill, provided they are free of debris and organic matter. Fills placed within 10 feet of finish pad grades or slope faces should contain no rocks over 12 inches in maximum dimension. If encountered, clayey soils layers (EI>51) should be placed at depth greater than 5 feet below finished grades where feasible. All structural fill should be compacted throughout to 90 percent of the ASTM D 1557 laboratory maximum density, at or slightly above optimum moisture.
Fill soils should be placed at a minimum of 90 percent relative compaction (based on ASTM D1557) and near or above optimum moisture content. Placement and compaction of fill should be performed in accordance with local grading ordinances under the observation and testing of the geotechnical consultant. 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 thickness.
Fill slope keyways will be necessary at the toe of all fill slopes and at fill-over-cut contacts. Keyway schematics, including dimensions and subdrain recommendations are provided in Appendix C. All keyways should be excavated into dense bedrock or dense older alluvium as determined by the geotechnical engineer.
Fills placed on slopes steeper than 5:1 (horizontal:vertical) should be benched into dense soils (see Appendix C for benching detail). Benching should be of sufficient depth to remove all loose material. A minimum bench height of 2 feet into approved material should be maintained at all times.
4.2.3 Shrinkage
The volume change of excavated onsite soils upon recompaction is expected to vary with materials, density, insitu moisture content, and location and compaction effort. The in-place and compacted densities of soil materials vary and accurate overall determination of shrinkage and bulking cannot be made. Therefore, we recommend site grading include, if possible, a balance area or ability to adjust grades slightly to accommodate some variation. Based on our review, we expect recompaction shrinkage (when recompacted to an average 93 percent of ASTM D1557) of 8- to 14-percent by volume for alluvial soils and 10 to 20 percent for any surficial topsoil/undocumented fill.
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4.2.4 Import Soils
Import soils and/or borrow sites, if needed, should be evaluated by us prior to import. Import soils should be uncontaminated, granular in nature, free of organic material (loss on ignition less-than 2 percent), have low expansion potential (with an Expansion Index less than 21) and have a low corrosion impact to the proposed improvements.
4.2.5 Utility Trenches
Utility trenches should be backfilled with compacted fill in accordance with the Standard Specifications for Public Works Construction, (“Greenbook”), 2021 Edition. Fill material above the pipe zone should be placed in lifts not exceeding 8 inches in uncompacted thickness and should be compacted to at least 90 percent relative compaction (ASTM D 1557) by mechanical means only. Site soils may generally be suitable as trench backfill provided these soils are screened of rocks over 1½ inches in diameter and organic matter. The upper 6 inches of backfill in all pavement areas should be compacted to at least 95 percent relative compaction.
Excavation of utility trenches should be performed in accordance with the project plans, specifications and the “Greenbook”. The contractor should be responsible for providing a "competent person" as defined in Article 6 of the California Construction Safety Orders. Contractors should be advised that sandy soils (such as fills generated from the onsite alluvium) could make excavations particularly unsafe if all safety precautions are not properly implemented. In addition, excavations at or near the toe of slopes and/or parallel to slopes may be highly unstable due to the increased driving force and load on the trench wall. Spoil piles from the excavation(s) and construction equipment should be kept away from the sides of the trenches. Leighton does not consult in the area of safety engineering.
4.2.6 Drainage
All drainage should be directed away from structures a minimum of 1% by means of approved permanent/temporary drainage devices. Adequate storm drainage of any proposed pad should be provided to avoid wetting of foundation soils.
Irrigation adjacent to buildings should be avoided when possible. As an option, sealed-bottom planter boxes and/or drought resistant vegetation should be used within 5-feet of buildings.
4.2.7 Slope Construction
Compacted fill up to 25 feet in height at 2:1 (horizontal:vertical) are considered grossly stable for static and pseudostatic conditions. Higher or steeper slopes should be subject to further review and evaluation. Any new 2:1 slopes using the onsite soils compacted to minimum 90 percent should also be stable under short and long term conditions. The outer portion of new fill slopes should be either Draft
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overbuilt by 2 feet (minimum) and trimmed back to the finished slope configuration or compacted in vertical increments of 5 feet (maximum) by a weighted sheepsfoot roller as the fill is placed. The slope face should then be track-walked by dozers of appropriate weight to achieve the final slope configuration and compaction to the slope face.
New fill slopes should be provided a toe of slope keyways as depicted in Appendix C. Any new fill slopes placed along existing fill slope, the minimum new fill width should be 8 feet. If fill is placed against existing cut slope (exposing older alluvium), the minimum fill width should be 15 feet per Appendix C. All cut slopes should be observed and mapped by a Leighton geologist to confirm the exposed conditions are stable and no minor fill width is left in place. In this case, when cutting an existing fill slope back into the fill core, a minimum remaining fill width of 15 feet is recommended. Any existing cut or fill slopes to remain in the current condition should be minimally scarified to remove minor erosion rills or vermin burrow, moisture conditioned thoroughly and compacted by track walking large dozer to achieve a compacted slope face.
Slope faces are inherently subject to erosion, particularly if exposed to rainfall and irrigation. Landscaping and slope maintenance should be conducted as soon as possible in order to increase long-term surficial stability. Berms should be provided at the top of fill slopes. Drainage should be directed such that surface runoff on the slope face is minimized
4.3 Foundation Design
4.3.1 Bearing and Lateral Pressures
Based on our analysis, single-family residential structures or light commercial structures may be founded on conventional or post-tensioned slab-on-grade systems based on prevailing finish pad soils conditions after grading. The compacted fill is anticipated to possess very low expansion potential. As such, we recommend that the structural consultant and/or foundation engineer presents foundation design categories (i.e. conventional or stiffened slab-on-grade design) based on actual expansion potential of subgrade soils of each pad at completion of grading. Foundation footings may be designed with the following geotechnical design parameters:
Allowable Bearing
Capacity:
2,000 psf at a minimum depth of embedment of 12 inches (min. width of 12 inches). This bearing capacity may be increased by ⅓ for short-term loading conditions (e.g., wind, seismic).
Sliding Coefficient: 0.35
Total Settlement: 2.0 inches
Differential Settlement: 1.0 inch in 40 feet
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The slab/foundation reinforcement should comply with the recommendations included in table below and the structural engineer’s requirements.
Table 3. Conventional Foundation Requirements
Conventional Foundation Minimum Requirements
Minimum Footing Reinforcement No. 4 rebar one (1) on top and one (1) on bottom.
Minimum Slab Thickness 4 inches (actual)
Minimum Slab Reinforcement No. 3 rebar spaced 18 inches on center each way.
Minimum Slab Subgrade
Moisture
110% optimum moisture to 12” depth prior to
placing concrete.
4.4 Retaining Walls
Retaining wall earth pressures are a function of the amount of wall yielding horizontally under load. If the wall can yield enough to mobilize full shear strength of backfill soils, then the wall can be designed for "active" pressure. If the wall cannot yield under the applied load, the shear strength of the soil cannot be mobilized and the earth pressure will be higher. Such walls should be designed for "at rest" conditions. If a structure moves toward the soils, the resulting resistance developed by the soil is the "passive" resistance.
Retaining walls backfilled with non-expansive soils should be designed using the following equivalent fluid pressures:
Table 4. Retaining Wall Design Earth Pressures (Static, Drained) Loading
Conditions
Equivalent Fluid Density (pcf)
Level Backfill 2:1 Backfill
Active 36 50
At-Rest 55 85
Passive* 300 150 (2:1, sloping down)
* This assumes level condition in front of the wall will remain for the duration of the project, not to exceed 3,500 psf at depth. If sloping down (2:1) grades exist in front of walls, then they should be designed using passive values reduced to ½ of level backfill passive resistance values.
Unrestrained (yielding) cantilever walls should be designed for the active equivalent-fluid weight value provided above for very low to low expansive soils that are free draining. In the design of walls restrained from movement at the top (non-yielding) such as basement or elevator pit/utility vaults, the at-rest equivalent fluid weight value should be used. Total depth of retained earth for design of cantilever walls should be measured as the vertical distance below the ground surface measured at the wall face for stem design, or measured at the heel of the footing for overturning and sliding calculations. Should a sloping backfill other than a 2:1 (horizontal:vertical) be constructed above the wall (or a Draft
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backfill is loaded by an adjacent surcharge load), the equivalent fluid weight values provided above should be re-evaluated on an individual case basis by us. Non-standard wall designs should also be reviewed by us prior to construction to check that the proper soil parameters have been incorporated into the wall design.
All retaining walls should be provided with appropriate drainage. The outlet pipe should be sloped to drain to a suitable outlet. Typical wall drainage design is illustrated in Appendix C, Retaining Wall Backfill and Subdrain Detail. Wall backfill should be nonexpansive (EI 21) sands compacted by mechanical methods to a minimum of 90 percent relative compaction (ASTM D 1557). Clayey site soils should not be used as wall backfill.
Walls should not be backfilled until wall concrete attains the 28-day compressive strength and/or as determined by the Structural Engineer that the wall is structurally capable of supporting backfill. Lightweight compaction equipment should be used, unless otherwise approved by the Structural Engineer.
4.5 Foundation Setback from Slopes
We recommend a minimum horizontal setback distance from the face of slopes for all structural footings (retaining and decorative walls, flatwork, building footings, pools, etc.).
This distance is measured from the outside bottom edge of the footing horizontally to the slope face (or the face of a retaining wall) and should be a minimum of H/2, where H is the slope height (in feet).
Table 5. Footing Setbacks
Slope Height Recommended Footing Setback
<5 feet 5 feet minimum
5 to 15 feet 7 feet minimum
>15 feet H/2, where H is the slope height, not to exceed 10 feet to 2:1 slope face
The soils within the structural setback area generally possess poor lateral stability and improvements (such as retaining walls, pools, sidewalks, fences, pavements, decorative flatwork, etc.) constructed within this setback area will be subject to lateral movement and/or differential settlement. Potential distress to such improvements may be mitigated by providing a deepened footing or a pier and grade-beam foundation system to support the improvement. The deepened footing should meet the setback described above.
Modifications of slope inclinations near foundations may increase the setback and should be reviewed by the design team prior to completion of design or implementation.
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4.6 Sulfate Attack
The results of limited laboratory testing indicated negligible sulfate exposure to concrete per ACI 318. Further testing should be performed during site grading to confirm solublesulfate content of near finish subgrade soils. Additional testing for general corrosion potential to ferrous materials should also be performed during grading.
4.7 Concrete Flatwork
Sidewalk/Flatwork should conform to applicable City and County standards. A representative of Leighton should verify subgrade soil expansion, moisture conditions and compaction prior to formwork and reinforcement placement. If subgrade soils possess expansion index greater than 21, we recommend a minimum 8-inch deepened edge be constructed for all flatwork to reduce moisture variation in subgrade soils along concrete edges adjacent to open (unfinished) or irrigated landscape areas.
Concrete flatwork should be constructed of uniformly cured, low-slump concrete and should contain sufficient control/contraction joints. Additional provisions such as ascending/descending slope conditions, perched (irrigation) water, special surcharge loading conditions, potential expansive soil pressure and differential settlement/heave should be incorporated into the design of exterior improvements. Additional exterior slab details are suggested in the American Concrete Institute (ACI) guidelines. Homeowners (HOA) should be advised of their maintenance responsibilities as well as geotechnical issues that could affect performance of site improvements.
4.8 Preliminary Pavement Design
The preliminary pavement design provided below is based on the locally accepted Caltrans Highway Design Manual and a preliminary R-value of 65 based on our laboratory testing on a representative soil sample. For planning and estimating purposes, the pavement sections are calculated based on assumed Traffic Indexes (TI).
Table 6. Asphalt Pavement Sections
General Traffic
Condition*
Traffic Index
(TI)**
Asphalt
Concrete*
(inches)
Aggregate Base*
(inches)
Local (Private) Street 6.0 3.0 6.0
Collector Street 7.0 3.0 6.0
*Per City minimum or as calculated
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Actual R-value of the subgrade soils will need to be verified after completion of site grading to finalize the pavement design. Pavement design and minimum sections should conform to applicable City standards, where applicable.
For rigid pavement design, we recommend that a minimum of 6 inches of PCC pavement be used, in high impact load areas or if to be subjected to truck traffic. The PCC pavement should be placed on a minimum 6-inch aggregate base. The PCC pavement may be placed directly on a compacted subgrade with an R-Value of 40 or higher. The PCC pavement should have a minimum of 28-day compressive strength of 3,250 psi.
Aggregate base should conform to the Standard Specifications for Public Works Construction (Green Book), 2021 Edition. Placement of concrete materials should follow applicable ACI and County standards.
The upper 6 inches of the subgrade soils should be moisture-conditioned to near optimum moisture content, compacted to at least 95 percent relative compaction (ASTM D1557) and kept in this condition until the pavement section is constructed. Minimum relative compaction requirements for aggregate base should be 95 percent of the maximum laboratory density as determined by ASTM D1557. If applicable, aggregate base should conform to the “Standard Specifications for Public Works Construction” (Greenbook) current edition or Caltrans Class 2 aggregate base and applicable City standards If pavement areas are adjacent to watered landscape areas, some deterioration of the subgrade load bearing capacity may result. Moisture control measures such as deepened curbs or other moisture barrier materials may be used to prevent the subgrade soils from becoming saturated. The use of concrete cutoff or edge barriers should be considered when pavement is planned adjacent to either open (unfinished) or irrigated landscaped areas.
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G E O T E C H N I C A L C O N S T R U C T I O N S E R V I C E S Geotechnical review is of paramount importance in engineering practice. Poor performances of many foundation and earthwork projects have been attributed to inadequate construction review. We recommend that Leighton be provided the opportunity to review the grading plan and foundation plan(s) prior to bid.
Reasonably-continuous construction observation and review during site grading and foundation installation allows for evaluation of the actual soil conditions and the ability to provide appropriate revisions where required during construction. Geotechnical conclusions and preliminary recommendations should be reviewed and verified by Leighton during construction, and revised accordingly if geotechnical conditions encountered vary from our findings and interpretations. Geotechnical observation and testing should be provided:
After completion of site clearing,
During preparation and overexcavation of surface soils as described herein, During compaction of all fill materials,
Testing of slab subgrade moisture content, prior to placement of vapor retarder, After excavation of all footings, and prior to placement of concrete, During utility trench backfilling and compaction, and When any unusual conditions are encountered.
Additional geotechnical exploration and analysis may be required based on final development plans, for reasons such as significant changes in proposed structure locations/footprints. We should review grading (civil) and foundation (structural) plans, and comment further on geotechnical aspects of this project.
5.0 Draft
Geotechnical Exploration 13177.002
Moreno Valley Town Center, Moreno Valley, California July 23, 2021 - 17 -
L I M I T A T I O N S
This report was necessarily based in part upon data obtained from a limited number of observances, site visits, soil samples, tests, analyses, histories of occurrences, spaced subsurface explorations and limited information on historical events and observations.
Such information is necessarily incomplete. The nature of many sites is such that differing characteristics can be experienced within small distances and under various climatic conditions. Changes in subsurface conditions can and do occur over time. This investigation was performed with the understanding that the subject site is proposed for residential and commercial development. The client is referred to Appendix D regarding important information provided by the GBA (Geoprofessional Business Association) on geotechnical engineering studies and reports and their applicability.
This report was prepared for Lewis Land Developers, LLC based on Lewis Land Developers, LLC needs, directions, and requirements at the time of our investigation.
This report is not authorized for use by, and is not to be relied upon by any party except Lewis Land Developers, LLC, and its successors and assigns as owner of the property, with whom Leighton and Associates, Inc. has contracted for the work. Use of or reliance on this report by any other party is at that party's risk. Unauthorized use of or reliance on this report constitutes an agreement to defend and indemnify Leighton and Associates, Inc. from and against any liability which may arise as a result of such use or reliance, regardless of any fault, negligence, or strict liability of Leighton and Associates, Inc.
6.0 Draft
Geotechnical Exploration 13177.002
Moreno Valley Town Center, Moreno Valley, California July 23, 2021 - 18 -
R E F E R E N C E S
ASCE, 2016, ASCE Standard 7-16, Minimum Design Loads for Buildings and Other Structures by Structural Engineering Institute
Bedrossian, T.L., and Roffers, P. D., 2012 Geologic Compilation of Quaternary Surficial Deposits in Southern California, Santa Ana 30’ X 30’ Quadrangle, CGS Special Report 217, December.
Earthquake Fault Zones, A Guide for Government Agencies, Property Oweners/Developers, and Geoscience Practitioners for Assessing Fault Rupture Hazards in California, Department of Conservation, California Geological Survey, Special Publication 42. Revised 2018.
California Building Code, (CBC) 2019, California Code of Regulations Title 24, Part 2, Volume 2 of 2.
California Department of Water Resources (CDWR) 2021, Water Data Library, http://www.water.ca.gov/waterdatalibrary/index.cfm, Data viewed July 13.
Public Works Standard, Inc., 2021, Greenbook, Standard Specifications for Public Works Construction: BNI Building News, Anaheim, California.
Riverside County Information Technology, 2021, Map My County (website), http://mmc.rivcoit.org/MMC_Public/Viewer.html?Viewer=MMC_Public.
Applied Technology Council (ATC), Hazards by Location (website), a graphical user interface to web services provided by the United States Geological Survey, (USGS), to calculate Seismic Response and Design Parameters based on ASCE 7-16 seismic procedures, https://hazards.atcouncil.org/#/seismic United States Geological Survey, (USGS), 2021, Unified Hazard Tool (website), https://earthquake.usgs.gov/hazards/interactive/
³ 0 2,000 4,000
Feet
Figure 1
Scale:
Leighton
Base Map: ESRI ArcGIS Online 2021
1 " = 2,000 '
Project: 13177.002 Eng/Geol: RIR
Map Saved as V:\Drafting\13177\002\Maps\13177-002_F01_SLM_2021-07-14.mxd on 7/15/2021 3:43:08 PM Author: Leighton Geomatics (kmanchikanti)
Date: July 2021
SITE LOCATION MAP
Lewis Moreno Valley Town Center
NW Corner of Alessandro Boulevard and Nason Street
Moreno Valley, County of Riverside, California
Approximate
Site Boundary
Map Saved as V:\Drafting\13177\002\Maps\13177-002_F02_BLM_2021-07-14.mxd on 7/20/2021 4:18:42 PM
BORING LOCATION MAP
Lewis Moreno Valley Town Center
NW Corner of Alessandro Boulevard and Nason Street
Moreno Valley, County of Riverside, California
Figure 2
³ 0 300 600
Feet
Scale:
Base Map: ESRI ArcGIS Online 2021
1 " = 300 '
Project: 13177.001 Eng/Geol: RBH
Author: (kmanchikanti)
Date: July 2021
Legend
&<
Approximate Location of Soil Boring
showing Total Depth in feet below
ground surface
&& Approximate Location of Percolation
Hole
Polygon Site Features
Approximate Site Boundary
LB-18
T.D 15'
P4
Leighton
?zE
gr
Qvof
Qvof
Qvof
Qvof
Qyf
Qyf
Qyf
Qya
Qya
Qvof
Qyf
gr
gr
gr
gr
gr
gr
gr
Qyf
Qvof
Qya
Qvof
Qvof
REGIONAL GEOLOGY MAP
Lewis Moreno Valley Town Center
NW Corner of Alessandro Boulevard and Nason Street
Moreno Valley, County of Riverside, California Base Map: USGS Topo Map Service from Esri, 2021 Reference: Socal Preliminary Geology, CGS 2010
Project: 13177.002 Eng/Geol: RIR
Document Path: V:\Drafting\13177\002\Maps\13177-002_F03_RGM_2021-07-15.mxd Author: (kmanchikanti) Scale:1 " = 2,000 ' Date: July 2021
Figure 3
Approximate
Site Limits
Geologic Units
Qyf, Young Alluvial Fan Deposits
! ! Qya, Young Alluvial Valley Deposits
Qvof, Very Old Alluvial Fan Deposits
gr, Granitic and other intrusive crystalline rocks
³ 0 2,000 4,000
Feet
Leighton
,
. . . . . . . .. . ... -
-
.. . . . . . .
..
. . . . . .
LIQUEFACTION HAZARD MAP
Lewis Moreno Valley Town Center
NW Corner of Alessandro Boulevard and Nason Street
Moreno Valley, County of Riverside, California Base Map: USGS Topo Map Service from Esri, 2021 Reference: Riverside County GIS Leighton
Project: 13177.002 Eng/Geol: RIR
Document Path: V:\Drafting\13177\002\Maps\13177-002_F04_LHM_2021-07-15.mxd Author: (kmanchikanti) Scale:1 " = 2,000 ' Date: July 2021
Figure 4
Approximate
Site Boundary
Liquefaction Susceptibility
Riverside County Liquefaction
Moderate
Low
³ 0 2,000 4,000
Feet
~
- .. , ,,. ....... s::: ISZS
------- =1==:c -- -
",. .. =-==- ,,,.-
--- €-
· ~ • ~
r-
'< I
-;:=-- -I ----'-
r
4 I
Well 0 ,s~,
Draft
Geotechnical Exploration 13177.002
Moreno Valley Town Center, Moreno Valley, California July 23, 2021
APPENDIX A
FIELD EXPLORATION / LOGS OF BORINGS
13 20
25 13
14 15
6 7
9 13
14 17
14 19
26 8
9 12
18 26
31 117
123
B-1
R-1
R-2
S-1
R-3
R-4
S-2
R-5
3 5
SILTY SAND, dense, pale brown to strong brown, slightly moist, Maximum Density = 134.5 pcf at Moisture = 7.9%, R-Value = 65, Fines = 24%, Sand = 70%, Gravel = 6%
SILTY SAND, medium dense, strong brown, moist
SILTY SAND, medium dense, strong brown, moist
SILTY SAND, medium dense, strong brown, moist
SILTY SAND, medium dense, strong brown, moist, Collapse =
1.14%
Well-graded SAND with silt, medium dense, yellowish brown, moist
Well-graded SAND with silt, medium dense, yellowish brown, moist
Well-graded SAND with silt, dense, yellowish brown, moist Boring Terminated at 26.5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings
MD, RV,
SA
CO
SM
SW-SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-01
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-.
-·
- .
- ".
-
-
-
-
9 11
15 19
32 47
9 11
10 9
15 20
9 10
13 120
120
117
R-1
R-2
S-1
R-3
S-2
2 5
6 SILTY SAND, dense, pale brown to strong brown, slightly moist SILTY SAND, medium dense, strong brown, moist
SILTY SAND, medium dense, strong brown, moist
SILTY SAND, medium dense, light brown to yellowish brown, moist, note: cleaner than Silty Sand above
SILTY SAND, medium dense, light brown to yellowish brown, moist, FINES = 18%
SILTY SAND, dense, light brown to yellowish brown, moist -200
SM
SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-02
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-.
-·
- .
-·.
-·
-
-
-.
-•
-·
-·.
-·
-
21 22
28 13
16 12
20 34
40 7
11 16
8 12
12 R-4 119
S-3
R-5
S-4
S-5
3 SILTY SAND, dense, light brown to yellowish brown, moist SILTY SAND with clay, medium dense, brown, moist, FINES = 24%, with some thin interbedded clayier layers and cleaner layers
SILTY SAND, dense, light brown to yellowish brown, slightly moist, Note: less fines than above, bordering on SW-SM
SILTY SAND with clay, medium dense to dense, reddish brown, moist
SILTY SAND with clay, medium dense, reddish brown, moist Boring Terminated at 51.5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings
SM -200
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-02
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
30 35
40 45
50 55
60 - .
- .
- ·
-
-
-•
-·
- .
- ·
- ·
-
-
-.
-
-
-
-
5 7
10 8
9 10
5 6
10 10
15 26
8 12
14 10
14 27
110
114
122
R-1
R-2
R-3
R-4
R-5
R-6
4 2
6 SILTY SAND, loose, pale brown to strong brown, slightly moist, Maximum Density = 133.6 pcf at Moisture = 7.5%, Fines = 27%, Sand = 69%, Gravel = 4%
SILTY SAND, medium dense, strong brown, moist
SILTY SAND, medium dense, strong brown, moist, Collapse =
2.79%
Well-graded SAND with silt and gravel, medium dense, light brown to yellowish brown, moist
SILTY SAND, medium dense, brown to strong brown, moist
SILTY SAND, medium dense, brown to strong brown, moist
Well-graded SAND with silt and gravel, medium dense, light brown to yellowish brown, moist
Boring Terminated at 21.5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings
MD, SA
CO
SM
SW-SM
SM
SW-SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-03
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 -
-
-
-
,,
,, - ,,
,, - ,,
-
-
-
-
,, - ,,
,,
- ,,
-
-
-
-
27 18
19 7
8 5
30 18
20 29
22 16
30 33
15 24
17 10
117
120
R-4
S-2
R-3
R-2
S-1
R-1
2 2
SILTY SAND with gravel, loose, pale brown to strong brown, slightly moist
Well-graded SAND with silt, medium dense, brown to yellowish SILTY SAND with gravel, medium dense, strong brown, moist SILTY SAND with gravel, medium dense, strong brown, moist SILTY SAND with gravel, medium dense, strong brown, moist brown, moist
Well-graded SAND with silt, medium dense, yellowish brown, slightly moist
SILTY SAND, medium dense, brown to strong brown, moist, fine sand
Backfilled with Soil Cuttings
No Groundwater Encountered
Boring Terminated at 21.5 Feet
SM
SW-SM
SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-04
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
gradual.
actual conditions encountered. Transitions between soil types may be and may change with time. The description is a simplification of the time of sampling. Subsurface conditions may differ at other locations This Soil Description applies only to a location of the exploration at the TYPE OF TESTS:
CU
CR
CO
CN
AL
-200
UNDRAINED TRIAXIAL
CORROSION
COLLAPSE
CONSOLIDATION
ATTERBERG LIMITS
% FINES PASSING
RV
PP
MD
H
EI
DS
R VALUE
POCKET PENETROMETER
MAXIMUM DENSITY
HYDROMETER
EXPANSION INDEX
DIRECT SHEAR
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
TUBE SAMPLE
SPLIT SPOON SAMPLE
RING SAMPLE
GRAB SAMPLE
CORE SAMPLE
BULK SAMPLE
T
S
R
G
C
B
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
UC
SG
SE
SA
UNCONFINED COMPRESSIVE STRENGTH
SPECIFIC GRAVITY
SAND EQUIVALENT
SIEVE ANALYSIS
5 0
30 25
20 15
10 I I I I I I I I I I I I I I I I I I I I I I I I I I I b " b" b' b' b ' b ' b ' b ' b ' b " ,__ _________________ _, t
24 12
9 5
50/6"
18 12
7 20
16 16
8 8
10 118
117
R-4
R-3
S-1
R-2
B-1
R-1
4 3
SILTY SAND with gravel, loose, pale brown to strong brown, slightly moist
SILTY SAND with gravel, medium dense, strong brown, moist, SILTY SAND with gravel, medium dense, strong brown, moist EI = 1 (Very Low)
Well-graded SAND with silt, medium dense, brown to yellowish SILTY SAND with gravel, medium dense, strong brown, moist brown, moist, with interbedded poorly-graded sand layers Well-graded SAND with silt, medium dense, yellowish brown, slightly moist
Backfilled with Soil Cuttings
No Groundwater Encountered
Boring Terminated at 16.5 Feet
EI
SM
SW-SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-05
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
gradual.
actual conditions encountered. Transitions between soil types may be and may change with time. The description is a simplification of the time of sampling. Subsurface conditions may differ at other locations This Soil Description applies only to a location of the exploration at the TYPE OF TESTS:
CU
CR
CO
CN
AL
-200
UNDRAINED TRIAXIAL
CORROSION
COLLAPSE
CONSOLIDATION
ATTERBERG LIMITS
% FINES PASSING
RV
PP
MD
H
EI
DS
R VALUE
POCKET PENETROMETER
MAXIMUM DENSITY
HYDROMETER
EXPANSION INDEX
DIRECT SHEAR
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
TUBE SAMPLE
SPLIT SPOON SAMPLE
RING SAMPLE
GRAB SAMPLE
CORE SAMPLE
BULK SAMPLE
T
S
R
G
C
B
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
UC
SG
SE
SA
UNCONFINED COMPRESSIVE STRENGTH
SPECIFIC GRAVITY
SAND EQUIVALENT
SIEVE ANALYSIS
5 0
30 25
20 15
10 I I I I I I I I I I I I I I I I I I I I I I I I I I I I . . . . . . >--------------------------1
t
5 8
10 7
6 8
7 10
10 3
5 6
18 26
32 5
8 13
12 37
50/6"
114
108
117
R-1
R-2
R-3
S-1
R-4
S-2
R-5
3 2
2 SILTY SAND with gravel, dense, pale brown to strong brown, slightly moist
SILTY SAND with gravel, medium dense, strong brown, moist SILTY SAND with gravel, medium dense, strong brown, moist, Collapse = 3.67%
Well-graded SAND with silt, medium dense, yellowish brown to light brown, moist
SILTY SAND, loose, brown, moist
SILTY SAND, dense, brown, moist
Well-graded SAND with silt, medium dense, brown, moist, with interbeds of Silty Sand
Well-graded SAND with silt, dense, brown, moist
Boring Terminated at 26.5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings
CO
SM
SW-SM
SM
SW-SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-06
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-
-
- .
-
-
4 4
- 4
4 - 4
4 4 -
4 -
-
6 5
12 9
12 14
5 7
8 10
11 13
15 19
18 9
15 21
116
118
112
R-1
R-2
S-1
R-3
S-2
R-4
3 3
5 SILTY SAND with gravel, loose, pale brown to strong brown, slightly moist
SILTY SAND with gravel, medium dense, strong brown, moist SILTY SAND with gravel, medium dense, strong brown, moist SILTY SAND, medium dense, strong brown, moist
SILTY SAND, medium dense, strong brown, moist, Collapse =
4.73%
SANDY SILT or SILTY SAND, dense, dark reddish brown, moist Well-graded SAND with silt and clay, medium dense, brown, moist
Boring Terminated at 21.5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings
CO
SM
ML
SW-SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-07
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-.
-·
-
-
-
~
- ~
~
- ~
-
-
-
-
4 5
7 3
5 7
4 5
9 5
6 9
16 26
36 105
112
113
113
B-1
R-1
R-2
R-3
R-4
R-5
6 5
5 5
SILTY SAND with gravel, loose, pale brown to strong brown, slightly moist
SILTY SAND with gravel, loose, strong brown, moist
SILTY SAND with gravel, loose, strong brown, moist, Collapse =
5.60%
SILTY SAND with gravel, loose, strong brown, moist
SILTY SAND, loose, strong brown, moist, Collapse = 4.77% SANDY SILT or SILTY SAND, dense, dark reddish brown,
slightly moist
Boring Terminated at 16.5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings
CO
CO
SM
ML
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG LB-08
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-.
-·
- .
-
-
-
-
-
-
-
-
-
Silty SAND with Gravel, medium dense, brown, slightly moist Boring Terminated at 7 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings After Percolation Test
SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-01
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Silty SAND with Gravel, medium dense, brown, slightly moist Boring Terminated at 5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings After Percolation Test
SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-02
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Silty SAND, loose, pale brown, slightly moist, fine sand Boring Terminated at 5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings After Percolation Test
SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-03
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-
-
-
-
-
-
-
-
-
-
-
-
6 10
13 R1
Silty SAND, loose, pale brown, slightly moist, fine sand, FINES = 42%
Boring Terminated at 5 Feet
No Groundwater Encountered
Backfilled with Soil Cuttings After Percolation Test
-200
SM
SAMPLE TYPES:
2R Drilling
* * * This log is a part of a report by Leighton and should not be used as a stand-alone document. * * * Content, % GEOTECHNICAL BORING LOG P-04
Logged By
Date Drilled
DP Feet
S (U.S.C.S.)
Log
Type of Tests
Graphic
pcf
Location
Dry Density
N
This Soil Description applies only to a location of the exploration at the time of sampling. Subsurface conditions may differ at other locations and may change with time. The description is a simplification of the actual conditions encountered. Transitions between soil types may be gradual.
TYPE OF TESTS:
-200
AL
CN
CO
CR
CU
% FINES PASSING
ATTERBERG LIMITS
CONSOLIDATION
COLLAPSE
CORROSION
UNDRAINED TRIAXIAL
DS
EI
H
MD
PP
RV
DIRECT SHEAR
EXPANSION INDEX
HYDROMETER
MAXIMUM DENSITY
POCKET PENETROMETER
R VALUE
Hole Diameter Moisture
Ground Elevation
Depth Blows Elevation Per 6 Inches
'
BULK SAMPLE
CORE SAMPLE
GRAB SAMPLE
RING SAMPLE
SPLIT SPOON SAMPLE
TUBE SAMPLE
B
C
G
R
S
T
DP
Hollow Stem Auger - 140lb - Autohammer - 30" Drop Soil Class. 7-1-21
SOIL DESCRIPTION
Sampled By
Drilling Co.
Project
Project No.
See Boring Location Map
Lewis MV Town Center
13177.002
Drilling Method
8" Sample No. Feet Attitudes
SA
SE
SG
UC
SIEVE ANALYSIS
SAND EQUIVALENT
SPECIFIC GRAVITY
UNCONFINED COMPRESSIVE STRENGTH
0 5
10 15
20 25
30 - .
-
-
-
-
-
-
-
-
-
-
-
-
-
-
Draft
Geotechnical Exploration 13177.002
Moreno Valley Town Center, Moreno Valley, California July 23, 2021
APPENDIX B
GEOTECHNICAL LABORATORY TEST RESULTS
Project Name: Tested By: M. Vinet Date: 7/15/21
Project No.: Checked By: M. Vinet Date: 7/16/21
Boring No.: LB-1 Sample Type: IN SITU
Sample No.: R-3 Depth (ft.) 10.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 115.4 Final Dry Density (pcf): 117.6 Initial Moisture (%): 7.4 Final Moisture (%) : 12.8
Initial Height (in.): 1.0000 Initial Void ratio: 0.4604 Initial Dial Reading (in): 0.0000 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.416 Initial Degree of Saturation (%): 43.5
1.050 0.9963 0.00 -0.37 -0.37
2.013 0.9927 0.00 -0.73 -0.73
H2O 0.9814 0.00 -1.86 -1.86
-1.14
Rev. 01-10
Lewis/MV Town Center/Geo
0.4333
0.0037
0.0073
0.0186
Silty Sand (SM), Brown.
13177.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
(ASTM D 4546) -- Method 'B'
Potential of Cohesive Soils
One-Dimensional Swell or Settlement
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.4550
0.4498
Final Reading
(in) Void Ratio
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 1.00
2.00 3.00
4.00 5.00
0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
Leighton
I
.. '1
r ~ ·
I
Project Name: Tested By: M. Vinet Date: 7/15/21
Project No.: Checked By: M. Vinet Date: 7/16/21
Boring No.: LB-3 Sample Type: IN SITU
Sample No.: R-2 Depth (ft.) 5.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 109.8 Final Dry Density (pcf): 114.6 Initial Moisture (%): 3.1 Final Moisture (%) : 15.8
Initial Height (in.): 1.0000 Initial Void ratio: 0.5355 Initial Dial Reading (in): 0.0000 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.416 Initial Degree of Saturation (%): 15.6
1.050 0.9928 0.00 -0.72 -0.72
2.013 0.9855 0.00 -1.45 -1.45
H2O 0.9580 0.00 -4.20 -4.20
-2.79
Rev. 01-10
Lewis/MV Town Center/Geo
0.4710
0.0072
0.0145
0.0420
Silty Sand (SM), Yellowish Brown.
13177.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
(ASTM D 4546) -- Method 'B'
Potential of Cohesive Soils
One-Dimensional Swell or Settlement
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.5245
0.5132
Final Reading
(in) Void Ratio
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 1.00
2.00 3.00
4.00 5.00
0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
Leighton
I
L..
......... I
I
j ..
Project Name: Tested By: M. Vinet Date: 7/15/21
Project No.: Checked By: M. Vinet Date: 7/16/21
Boring No.: LB-6 Sample Type: IN SITU
Sample No.: R-2 Depth (ft.) 5.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 100.6 Final Dry Density (pcf): 105.5 Initial Moisture (%): 4.4 Final Moisture (%) : 18.2
Initial Height (in.): 1.0000 Initial Void ratio: 0.6750 Initial Dial Reading (in): 0.0000 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.416 Initial Degree of Saturation (%): 17.5
1.050 0.9950 0.00 -0.50 -0.50
2.013 0.9906 0.00 -0.94 -0.94
H2O 0.9542 0.00 -4.58 -4.58
-3.67
Rev. 01-10
Lewis/MV Town Center/Geo
0.5983
0.0050
0.0094
0.0458
Silty Sand (SM), Yellowish Brown.
13177.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
(ASTM D 4546) -- Method 'B'
Potential of Cohesive Soils
One-Dimensional Swell or Settlement
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.6666
0.6592
Final Reading
(in) Void Ratio
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 1.00
2.00 3.00
4.00 5.00
0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
Leighton
I
..
----.......... I - I
' l
Project Name: Tested By: M. Vinet Date: 7/15/21
Project No.: Checked By: M. Vinet Date: 7/16/21
Boring No.: LB-7 Sample Type: IN SITU
Sample No.: R-3 Depth (ft.) 10
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 104.1 Final Dry Density (pcf): 111.2 Initial Moisture (%): 4.0 Final Moisture (%) : 16.5
Initial Height (in.): 1.0000 Initial Void ratio: 0.6196 Initial Dial Reading (in): 0.0000 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.416 Initial Degree of Saturation (%): 17.6
1.050 0.9927 0.00 -0.73 -0.73
2.013 0.9827 0.00 -1.73 -1.73
H2O 0.9362 0.00 -6.38 -6.38
-4.73
Rev. 01-10
Lewis/MV Town Center/Geo
0.5163
0.0073
0.0173
0.0638
Silty Sand (SM), Brown.
13177.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
(ASTM D 4546) -- Method 'B'
Potential of Cohesive Soils
One-Dimensional Swell or Settlement
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.6078
0.5916
Final Reading
(in) Void Ratio
-8.00
-7.00
-6.00
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 1.00
2.00 3.00
0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
Leighton
I
I.
I ' 1 I
I
I
Project Name: Tested By: M. Vinet Date: 7/15/21
Project No.: Checked By: M. Vinet Date: 7/16/21
Boring No.: LB-8 Sample Type: IN SITU
Sample No.: R-2 Depth (ft.) 5.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 100.7 Final Dry Density (pcf): 110.9 Initial Moisture (%): 6.4 Final Moisture (%) : 17.4
Initial Height (in.): 1.0000 Initial Void ratio: 0.6737 Initial Dial Reading (in): 0.0000 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.416 Initial Degree of Saturation (%): 25.8
1.050 0.9774 0.00 -2.26 -2.26
2.013 0.9615 0.00 -3.85 -3.85
H2O 0.9077 0.00 -9.23 -9.23
-5.60
Rev. 01-10
Lewis/MV Town Center/Geo
0.5193
0.0226
0.0385
0.0923
Silty Sand (SM), Brown.
13177.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
(ASTM D 4546) -- Method 'B'
Potential of Cohesive Soils
One-Dimensional Swell or Settlement
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.6359
0.6093
Final Reading
(in) Void Ratio
-10.00
-9.00
-8.00
-7.00
-6.00
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
Leighton
I
• '\.
( '" 111
I
I
j ..
Project Name: Tested By: M. Vinet Date: 7/15/21
Project No.: Checked By: M. Vinet Date: 7/16/21
Boring No.: LB-8 Sample Type: IN SITU
Sample No.: R-4 Depth (ft.) 10.0
Sample Description:
Source and Type of Water Used for Inundation: Arrowhead ( Distilled ) ** Note: Loading After Wetting (Inundation) not Performed Using this Test Method.
Initial Dry Density (pcf): 102.9 Final Dry Density (pcf): 111.5 Initial Moisture (%): 6.2 Final Moisture (%) : 18.0
Initial Height (in.): 1.0000 Initial Void ratio: 0.6385 Initial Dial Reading (in): 0.0000 Specific Gravity (assumed): 2.70 Inside Diameter of Ring (in): 2.416 Initial Degree of Saturation (%): 26.3
1.050 0.9827 0.00 -1.73 -1.73
2.013 0.9692 0.00 -3.08 -3.08
H2O 0.9230 0.00 -7.70 -7.70
-4.77
Rev. 01-10
Lewis/MV Town Center/Geo
0.5123
0.0173
0.0308
0.0770
Silty Sand (SM), Brown.
13177.002
Swell (+)
Settlement (-)
% of Sample
Thickness
Load
Compliance
(%)
Apparent
Thickness
(in)
(ASTM D 4546) -- Method 'B'
Potential of Cohesive Soils
One-Dimensional Swell or Settlement
Percent Swell / Settlement After Inundation =
Corrected
Deformation
(%)
Pressure (p)
(ksf)
0.6101
0.5880
Final Reading
(in) Void Ratio
-10.00
-9.00
-8.00
-7.00
-6.00
-5.00
-4.00
-3.00
-2.00
-1.00
0.00 0.010 0.100 1.000 10.000
Deformation %
Log Pressure (ksf)
Deformation % - Log Pressure Curve
Inundate With
Distilled Water
Leighton
I
ll
" '-
-I - ,
I
I
j l
Project Name: Tested By: MRV Date: 07/15/21
Project No.: 13177.002 Checked By: MRV Date: 07/16/21
Boring No.: LB-1 Depth (feet): 0.0
Sample No.: B-1
Soil Identification: Silty Sand (SM), Dark Yellowish Brown.
Whole Sample Sample Passing
#4 Whole Sample Sample passing #4
M M Wt. of Air-Dry Soil + Cont.(g) 2029.2 991.3
2029.2 991.3 Wt. of Dry Soil + Cont. (g) 2004.3 991.3
666.4 666.4 Wt. of Container No._____(g) 666.4 666.4
1337.4 324.9 Moisture Content (%) 1.9 0.0
M
909.4
666.4
243.0
(mm.)
1 1/2"
1"
3/4"
1/2"
3/8"
#4
#8
#16
#30
#50
#100
#200
GRAVEL: 6 %
SAND: 70 %
FINES: 24 %
GROUP SYMBOL: SM N/A
N/A
Remarks:
243.1
67.3 112.8
160.7
207.4
0.075
PAN
20.1 45.3
4.750 75.4
2.360
1.180
0.600
0.300
0.150
Passing #4 Material After Wet Sieve
37.500
U. S. Sieve Size
25.000
19.000
12.500
9.500
Whole Sample
96.6 100.0
94.4 86.3
23.8 100.0
47.7 34.1
Wt. Air-Dried Soil + Cont.(g)
98.5 Cumulative Weight of Dry Soil Retained (g)
Sample Passing #4
PARTICLE-SIZE DISTRIBUTION (GRADATION)
ASTM D 6913
Container No.:
Lewis/MV Town Center/Geo
Moisture Contents Calculation of Dry Weights
of SOILS USING SIEVE ANALYSIS
Dry Wt. of Soil (g)
0.0 Wt. of Container (g)
Container No.
100.0
74.8 61.6
Percent Passing
(%)
Wt. of Dry Soil + Container (g)
Wt. of Container (g)
Dry Wt. of Soil Retained on # 200 Sieve (g)
28.0 Cu = D60/D10 =
Cc = (D30)²/(D60*D10) =
6 : 70 : 24
B-1
Jul-21
Boring No.:
Depth (feet): 0.0 Soil Type :
Project Name:
PARTICLE - SIZE
DISTRIBUTION
ASTM D 6913
Soil Identification: Silty Sand (SM), Dark Yellowish Brown.
SM
GR:SA:FI : (%)
Lewis/MV Town Center/Geo
Project No.:
LB-1 Sample No.:
13177.002
SAND
FINE SILT
HYDROMETER
3.0" 1 1/2" 3/4" 3/8" #4 #8 #16 #30 #50 #100 #200
U.S. STANDARD SIEVE OPENING U.S. STANDARD SIEVE NUMBER
GRAVEL FINES
COARSE FINE COARSE MEDIUM CLAY
0 10
20 30
40 50
60 70
80 90
100
100.000 10.000 1.000 0.100 0.010 0.001
PERCENT FINER BY WEIGHT
PARTICLE - SIZE (mm)
"
Sieve; LB-1, B-1 (07-01-21)
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Project Name: Tested By: MRV Date: 07/15/21
Project No.: 13177.002 Checked By: MRV Date: 07/16/21
Boring No.: LB-3 Depth (feet): 0.0
Sample No.: B-1
Soil Identification: Silty Sand (SM), Dark Yellowish Brown.
Whole Sample Sample Passing
#4 Whole Sample Sample passing #4
B B Wt. of Air-Dry Soil + Cont.(g) 2024.7 990.3
2024.7 990.3 Wt. of Dry Soil + Cont. (g) 1995.4 990.3
673.2 673.2 Wt. of Container No._____(g) 673.2 673.2
1322.4 317.1 Moisture Content (%) 2.2 0.0
B
903.2
673.2
230.0
(mm.)
1 1/2"
1"
3/4"
1/2"
3/8"
#4
#8
#16
#30
#50
#100
#200
GRAVEL: 4 %
SAND: 69 %
FINES: 27 %
GROUP SYMBOL: SM N/A
N/A
Remarks:
226.9
48.2 78.2
123.5
179.6
0.075
PAN
10.6 25.2
4.750 48.0
2.360
1.180
0.600
0.300
0.150
Passing #4 Material After Wet Sieve
37.500
U. S. Sieve Size
25.000
19.000
12.500
9.500
Whole Sample
98.1 100.0
96.4 90.6
27.4 100.0
58.9 41.8
Wt. Air-Dried Soil + Cont.(g)
99.2 Cumulative Weight of Dry Soil Retained (g)
Sample Passing #4
PARTICLE-SIZE DISTRIBUTION (GRADATION)
ASTM D 6913
Container No.:
Lewis/MV Town Center/Geo
Moisture Contents Calculation of Dry Weights
of SOILS USING SIEVE ANALYSIS
Dry Wt. of Soil (g)
0.0 Wt. of Container (g)
Container No.
100.0
81.7 72.6
Percent Passing
(%)
Wt. of Dry Soil + Container (g)
Wt. of Container (g)
Dry Wt. of Soil Retained on # 200 Sieve (g)
19.0 Cu = D60/D10 =
Cc = (D30)²/(D60*D10) =
4 : 69 : 27
B-1
Jul-21
Boring No.:
Depth (feet): 0.0 Soil Type :
Project Name:
PARTICLE - SIZE
DISTRIBUTION
ASTM D 6913
Soil Identification: Silty Sand (SM), Dark Yellowish Brown.
SM
GR:SA:FI : (%)
Lewis/MV Town Center/Geo
Project No.:
LB-3 Sample No.:
13177.002
SAND
FINE SILT
HYDROMETER
3.0" 1 1/2" 3/4" 3/8" #4 #8 #16 #30 #50 #100 #200
U.S. STANDARD SIEVE OPENING U.S. STANDARD SIEVE NUMBER
GRAVEL FINES
COARSE FINE COARSE MEDIUM CLAY
0 10
20 30
40 50
60 70
80 90
100
100.000 10.000 1.000 0.100 0.010 0.001
PERCENT FINER BY WEIGHT
PARTICLE - SIZE (mm)
"
Sieve; LB-3, B-1 (07-01-21)
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Project Name: Tested By: M. Vinet Date: 7/15/21
Project No. : Checked By: M. Vinet Date: 7/16/21
Boring No.: Depth: 5.0
Sample No. : Location:
Sample Description:
Dry Wt. of Soil + Cont. (gm.)
Wt. of Container No. (gm.)
Dry Wt. of Soil (gm.)
Weight Soil Retained on #4 Sieve
Percent Passing # 4
in distilled water for the period of 24 h or expansion rate < 0.0002 in./h.
Rev. 03-08
SPECIMEN INUNDATION
65.3 Dry Wt. of Soil + Cont. (gm.)
8.5 349.9
326.4
0.461
49.9 200.0
635.0
131.1
Elapsed Time
(min.)
Dial Readings
(in.)
49.8 80.1
Pressure
(psi)
Total Porosity 0.316
2.70 382.5
200.0
13.7 0.316
65.5 EXPANSION INDEX of SOILS
Silty Sand (SM), Dark Yellowish Brown.
MOLDED SPECIMEN
4.01 1.0000
Container No. 10
Specimen Diameter (in.)
Wt. Comp. Soil + Mold (gm.)
200.0
N/A
Lewis/MV Town Center/Geo
13177.002
LB-5
B-1
ASTM D 4829
96.9 4.01
2.70 2555.6
0.0 615.0
2555.6
80.2 1.0010
635.0
Before Test After Test
Wet Wt. of Soil + Cont. (gm.)
10 0.463
Dry Density (pcf)
Wet Density (pcf)
Specific Gravity (Assumed)
Specimen Height (in.)
Wt. of Mold (gm.)
7/15/21
115.4
Moisture Content (%)
Date
10:00
Void Ratio
Pore Volume (cc)
Degree of Saturation (%) [ S meas]
125.2
Time
7/16/21 9:00
1.0 1.0
7/15/21 10:10 1.0
1.0 Expansion Index ( Report ) = Nearest Whole Number or Zero (0) if Initial Height is > than Final Height 1 Add Distilled Water to the Specimen
Wt. of Container (gm.)
115.3
0.5000
10 0.5000
7/16/21 0.5010
0 1310
Expansion Index (EI meas) = ((Final Rdg - Initial Rdg) / Initial Thick.) x 1000 8:00
1370 0.5010
1.0 Leighton
Project Name: Date: 7/14/21
Project Number: 13177.002 Technician: F. Mina
Boring Number: LB-1 Depth (ft.): 0.0
Sample Number: B-1 Sample Location:
Sample Description: Silty Sand (SM), Dark Yellowish Brown
TEST SPECIMEN A B C
MOISTURE AT COMPACTION % 7.1 8.2 9.2
HEIGHT OF SAMPLE, Inches 2.50 2.50 2.52
DRY DENSITY, pcf 119.8 121.2 120.4
COMPACTOR AIR PRESSURE, psi 200 175 150
EXUDATION PRESSURE, psi 696 348 144
EXPANSION, Inches x 10exp-4 0 0 0
STABILITY Ph 2,000 lbs (160 psi) 23 30 57
TURNS DISPLACEMENT 4.84 5.05 5.55
R-VALUE UNCORRECTED 75 68 45
R-VALUE CORRECTED 75 68 45
DESIGN CALCULATION DATA a b c
GRAVEL EQUIVALENT FACTOR 1.0 1.0 1.0
TRAFFIC INDEX 5.0 5.0 5.0
STABILOMETER THICKNESS, ft. 0.39 0.51 0.88
EXPANSION PRESSURE THICKNESS, ft. 0.00 0.00 0.00
EXPANSION PRESSURE CHART EXUDATION PRESSURE CHART
R-VALUE BY EXPANSION: N/A
R-VALUE BY EXUDATION: 65
EQUILIBRIUM R-VALUE: 65
R-VALUE TEST RESULTS
ASTM D 2844
Lewis/MV Town Center/Geo
N/A
0.00 0.50
1.00 1.50
2.00 2.50
3.00 3.50
4.00 0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00
COVER THICKNESS BY EXPANSION in
feet
COVER THICKNESS BY STABILOMETER in
feet
0 10
20 30
40 50
60 70
80 90
800 700 600 500 400 300 200 100 0
R-VALUE
EXUDATION PRESSURE (psi)
Leighton
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Project Name: Lewis/MV Town Center/Geo Tested By : M. Vinet Date: 07/16/21 Project No. : 13177.002 Data Input By: M. Vinet Date: 07/16/21 Boring No. LB-3
Sample No. B-1
Sample Depth (ft) 0.0
100.00
100.00
0.00 0.00
100.00
1 1
850
Timer
45 25.1158
25.1099
0.0059
242.79
243
ml of Extract For Titration (B) 30
ml of AgNO3 Soln. Used in Titration (C) 0.8
PPM of Chloride (C -0.2) * 100 * 30 / B 60
PPM of Chloride, Dry Wt. Basis 60
7.20 21.0
TESTS for SULFATE CONTENT
CHLORIDE CONTENT and pH of SOILS
SULFATE CONTENT, DOT California Test 417, Part II
Soil Identification:
Moisture Content (%)
Temperature °C
pH Value
pH TEST, DOT California Test 643
Dry Weight of Soil + Container (g)
Weight of Container (g)
Duration of Combustion (min)
PPM of Sulfate, Dry Weight Basis
Wt. of Crucible (g)
Silty Sand (SM)
Wt. of Crucible + Residue (g)
Wet Weight of Soil + Container (g)
Wt. of Residue (g) (A)
Beaker No.
Crucible No.
Furnace Temperature (°C)
Time In / Time Out
Weight of Soaked Soil (g)
PPM of Sulfate (A) x 41150
CHLORIDE CONTENT, DOT California Test 422
Leighton
Project Name: Tested By : M. Vinet Date:
Project No. : Data Input By: M. Vinet Date:
Boring No.: Depth (ft.) :
Sample No. :
Soil Identification:*
*California Test 643 requires soil specimens to consist only of portions of samples passing through the No. 8 US Standard Sieve before resistivity testing. Therefore, this test method may not be representative for coarser materials.
10.00 6500 Wt. of Container (g)
0.00 100.00
Moisture Content (%) (MCi)
Wet Wt. of Soil + Cont. (g)
Specimen
No.
1 2
Water
Added (ml)
(Wa)
50 Adjusted
Moisture
Content
(MC) Dry Wt. of Soil + Cont. (g)
6500
1.000
Chloride Content
(ohm-cm)
29.80 Moisture Content Sulfate Content
5 Min. Resistivity
DOT CA Test 417 Part II DOT CA Test 422 DOT CA Test 643 (%) (ppm) (ppm)
DOT CA Test 643
4 83
116
149
A
3 23.20 2100 500.00
2800
2100 23.2 243 60 7.20 21.0
SOIL RESISTIVITY TEST
DOT CA TEST 643
pH Temp. (°C)
Soil pH
2800
2100
100.00
0.00 MC =(((1+Mci/100)x(Wa/Wt+1))-1)x100
Lewis/MV Town Center/Geo 07/16/21
07/16/21
0.0 13177.002
LB-3
B-1
Container No.
Initial Soil Wt. (g) (Wt)
2400 2400 Box Constant
Silty Sand (SM)
Resistance
Reading
(ohm)
16.60 Soil
Resistivity
(ohm-cm)
0 1000
2000
3000
4000
5000
6000
7000
0.0 5.0 10.0 15.0 20.0 25.0 30.0 35.0
Soil Resistivity (ohm-cm)
Moisture Content (%)
Minimum resistivity
read here
Leighton
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Draft
Geotechnical Exploration 13177.002
Moreno Valley Town Center, Moreno Valley, California July 23, 2021
APPENDIX C
EARTHWORK AND GRADING SPECIFICATIONS
Draft
Geotechnical Exploration 13177.002
Moreno Valley Town Center, Moreno Valley, California July 23, 2021
APPENDIX D
GBA IMPORTANT INFORMATION ABOUT THIS
GEOTECHNICAL ENGINEERING REPORT
- 35 -
Appendix 4: Historical Site Conditions
Phase I Environmental Site Assessment or Other Information on Past Site Use - 36 -
Appendix 5: LID Infeasibility
LID Technical Infeasibility Analysis
- 37 -
Appendix 6: BMP Design Details
BMP Sizing, Design Details and other Supporting Documentation Santa Ana Watershed
These worksheets are to be used to determine the required Design Capture Volume (VBMP)
or the
Design Flow Rate (QBMP)
for BMPs in the Santa Ana Watershed
To verify which watershed your project is located within, visit www.rcflood.org/npdes
and use the 'Locate my Watershed' tool
to access the worksheets for the Santa Ana Watershed
VBMP and QBMP worksheets
If your project is not located in the Santa Ana Watershed, www.rcflood.org/npdes/developers.aspx
Do not use these worksheets! Instead visit
To access worksheets applicable to your watershed
Use the tabs across the bottom
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
1 300,999.60 Mixed Surface Types 0.7 0.49 148661.9
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
300999.6 148661.9 0.66 8176.4 1
Notes:
BMP Identification
Drainage Management Area Tabulation
Design Rainfall Depth
BMP NAME / ID Lot/BMP #1
Must match Name/ID used on BMP Design Calculation Sheet Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
Total
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Insert additional rows if needed to accommodate all DMAs draining to the BMP Proposed Volume must be greater than the Design Capture Volume I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
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Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
2 375,051.60 Mixed Surface Types 0.7 0.49 185235.7
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
375051.6 185235.7 0.66 10188 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #2
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 5/20/2022
I
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Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
3a 102,801.60 Mixed Surface Types 0.7 0.49 50773.1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
102801.6 50773.1 0.66 2792.5 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #3a
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 5/20/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
3b 147,232.80 Mixed Surface Types 0.7 0.49 72717.4
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
147232.8 72717.4 0.66 3999.5 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #3b
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
4a 75,358.80 Mixed Surface Types 0.2 0.17 12846
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
75358.8 12846 0.66 706.5 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #4a
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
4b 77,101.20 Mixed Surface Types 0.2 0.17 13143
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
77101.2 13143 0.66 722.9 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #4b
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
5 324,522.00 Mixed Surface Types 0.7 0.49 160279.5
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
324522 160279.5 0.66 8815.4 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #5
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
6 341,510.40 Mixed Surface Types 0.7 0.49 168669.9
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
341510.4 168669.9 0.66 9276.8 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #6
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
7a 207,781.20 Mixed Surface Types 0.85 0.66 137399.3
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
207781.2 137399.3 0.66 7557 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #7a
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
7b 485,258.40 Mixed Surface Types 0.85 0.66 320886.5
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
485258.4 320886.5 0.66 17648.8 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID Lot/BMP #7b
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
Lot/BMP #8
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
8 59,677.20 Mixed Surface Types 0.2 0.17 10172.8
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
59677.2 10172.8 0.66 559.5 1
Notes:
Total
Proposed Volume must be greater than the Design Capture Volume Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP BMP Identification
BMP NAME / ID
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
Lot/BMP ROW South
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
ROW
South 137,649.60 Mixed Surface Types 0.7 0.49 67984.3
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
137649.6 67984.3 0.66 3739.1 1
Notes:
Proposed Volume must be greater than the Design Capture Volume Insert additional rows if needed to accommodate all DMAs draining to the BMP Total
BMP Identification
BMP NAME / ID
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Drainage Management Area Tabulation
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
Lot/BMP ROW North
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
ROW
North 175,982.40 Mixed Surface Types 0.7 0.49 86916.7
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
175982.4 86916.7 0.66 4780.4 1
Notes:
Proposed Volume must be greater than the Design Capture Volume Insert additional rows if needed to accommodate all DMAs draining to the BMP Total
BMP Identification
BMP NAME / ID
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Drainage Management Area Tabulation
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
Lot/BMP ROW East
D85= 0.66 inches
DMA
Type/ID
DMA Area
(square feet)
Post-Project Surface
Type
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Storm
Depth (in)
Design Capture
Volume, VBMP
(cubic feet)
Proposed
Volume on
Plans (cubic
feet)
ROW East 221,720.40 Mixed Surface Types 0.7 0.49 109506.4 1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
221720.4 109506.4 0.66 6022.9 1
Notes:
Proposed Volume must be greater than the Design Capture Volume Insert additional rows if needed to accommodate all DMAs draining to the BMP Total
BMP Identification
BMP NAME / ID
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
85th Percentile, 24-hour Rainfall Depth,
from the Isohyetal Map in Handbook Appendix E
Drainage Management Area Tabulation
Designed by Samuel J. Jacoby, PE, QSD Case No
Company Project Number/Name Moreno Valley Town Center, for Lewis Management Santa Ana Watershed - BMP Design Volume, VBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name Cannon Corp 8/15/2022
I
-- I
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Ir r
Date
I = 0.20 in/hr
DMA
Type/ID
DMA Area
(square feet)
Post-Project
Surface Type
(use pull-down menu)
Effective
Imperivous
Fraction, If
DMA
Runoff
Factor
DMA Areas x
Runoff Factor
Design
Rainfall
Intensity
(in/hr)
Design Flow
Rate (cfs)
Proposed
Flow Rate
(cfs)
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 1
1 0 0 0.20
Notes:
Drainage Management Area Tabulation
Insert additional rows if needed to accommodate all DMAs draining to the BMP Design Rainfall Intensity
Total DMAs
BMP Identification
BMP NAME / ID
Must match Name/ID used on BMP Design Calculation Sheet Design Rainfall Depth
Designed by Case No
Company Project Number/Name
Santa Ana Watershed - BMP Design Flow Rate, QBMP Legend:
Required Entries
Calculated Cells
(Note this worksheet shall only be used in conjunction with BMP designs from the LID BMP Design Handbook ) Company Name
I
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" "
" "
" "
" "
" "
" "
" "
" "
" "
" "
~ ~ ~ " ~ ~ ~
BMP ID
1 Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 6.9 acres
Enter VBMP determined from Section 2.1 of this Handbook VBMP= 8,176 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 30.0 ft Total Effective Depth, dE
dE = 1.33 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 6,164 ft2
A= 7,560 ft2
Minimum Required Length of Bioretention Facility, L L = 205.5 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 30 ft x 252 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
I I
@
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I I
BMP ID
2 Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 8.61 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 10,188 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 46.0 ft Total Effective Depth, dE
dE = 1.33 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 7,633 ft2
A= 10,120 ft2
Minimum Required Length of Bioretention Facility, L L = 165.9 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 46 ft x 220 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
I I
@
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I I
BMP ID
3a
Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 2.36 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 2,793 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 25.0 ft Total Effective Depth, dE
dE = 1.32 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 2,113 ft2
A= 2,600 ft2
Minimum Required Length of Bioretention Facility, L L = 84.5 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 25 ft x 104 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
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@
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I I
BMP ID
3b
Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 3.38 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 4,000 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 30.0 ft Total Effective Depth, dE
dE = 1.33 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 3,015 ft2
A= 3,150 ft2
Minimum Required Length of Bioretention Facility, L L = 100.5 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 30 ft x 105 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
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BMP ID
4a
Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 1.73 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 707 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 26.0 ft Total Effective Depth, dE
dE = 1.32 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 534 ft2
A= 1,040 ft2
Minimum Required Length of Bioretention Facility, L L = 20.5 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 26 ft x 40 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
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@
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BMP ID
4b
Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 1.77 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 723 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 20.0 ft Total Effective Depth, dE
dE = 1.32 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 550 ft2
A= 800 ft2
Minimum Required Length of Bioretention Facility, L L = 27.5 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 20 ft x 40 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
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BMP ID
5 Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 7.45 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 8,815 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 45.0 ft Total Effective Depth, dE
dE = 1.33 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 6,607 ft2
A= 8,100 ft2
Minimum Required Length of Bioretention Facility, L L = 146.8 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 45 ft x 180 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
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@
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BMP ID
6 Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 7.84 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 9,277 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 45.0 ft Total Effective Depth, dE
dE = 1.33 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 6,952 ft2
A= 8,325 ft2
Minimum Required Length of Bioretention Facility, L L = 154.5 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 45 ft x 185 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
I I
@
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BMP ID
7a
Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 4.77 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 7,557 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 40.0 ft Total Effective Depth, dE
dE = 1.33 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 5,672 ft2
A= 7,000 ft2
Minimum Required Length of Bioretention Facility, L L = 141.8 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 40 ft x 175 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
I I
@
0 -
I l
I I
BMP ID
7b
Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 11.14 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 17,649 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 55.0 ft Total Effective Depth, dE
dE = 1.34 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 13,198 ft2
A= 16,775 ft2
Minimum Required Length of Bioretention Facility, L L = 240.0 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes:
Required Entries
Minimum Surface Area, Am
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Type of Bioretention Facility Design
VBMP (ft3
)
AM (ft2
) =
Proposed Surface Area
dE (ft)
Bioretention Facility Properties
55 ft x 305 ft
Bioretention Facility - Design Procedure Legend:
Cannon Corp
Moreno Valley Town Center, for Lewis Management
Design Volume
Calculated Cells
Bioretention Facility Surface Area
Side Slopes in Bioretention Facility
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
I I
@
0 -
I l
I I
BMP ID
8 Company Name: Date: 8/15/2022
Designed by: County/City Case No.:
Enter the area tributary to this feature AT= 1.37 acres Enter VBMP determined from Section 2.1 of this Handbook VBMP= 560 ft3 Depth of Soil Filter Media Layer dS
= 1.5 ft
Top Width of Bioretention Facility, excluding curb wT = 40.0 ft Total Effective Depth, dE
dE = 1.33 ft
dE = [(0.3) x dS + (0.4) x 1] + 0.5 dE = 1.35 ft
AM = 420 ft2
A= 1,760 ft2
Minimum Required Length of Bioretention Facility, L L = 10.5 ft z = 4 :1
Diameter of Underdrain 6 inches
Longitudinal Slope of Site (3% maximum) 2 %
6" Check Dam Spacing 25 feet
Describe Vegetation:
Notes: 40 ft x 44 ft
Bioretention Facility Properties
Side Slopes in Bioretention Facility
Proposed Surface Area
Design Volume
Type of Bioretention Facility Design
Bioretention Facility Surface Area
dE = (0.3) x dS + (0.4) x 1 - (0.7/wT) + 0.5
Minimum Surface Area, Am
AM (ft2) =
VBMP (ft3)
dE (ft)
Moreno Valley Town Center, for Lewis Management
Bioretention Facility - Design Procedure Legend:
Required Entries
Calculated Cells
Cannon Corp
Side slopes required (parallel to parking spaces or adjacent to walkways) No side slopes required (perpendicular to parking space or Planter Boxes) Riverside County Best Management Practice Design Handbook JUNE 2010
I I
@
0 -
I l
I I
Developed Cover Types Effective Impervious Fraction
Roofs 1.00
Concrete or Asphalt 1.00
Grouted or Gapless Paving Blocks 1.00
Compacted Soil (e.g. unpaved parking) 0.40
Decomposed Granite 0.40
Permeable Paving Blocks w/ Sand Filled Gap 0.25
Class 2 Base 0.30
Gravel or Class 2 Permeable Base 0.10
Pervious Concrete / Porous Asphalt 0.10
Open and Porous Pavers 0.10
Turf block 0.10
Ornamental Landscaping 0.10
Natural (A Soil) 0.03
Natural (B Soil) 0.15
Natural (C Soil) 0.30
Natural (D Soil) 0.40
Mixed Surface Types
Effective Impervious Fraction
Use this table to determine the effective impervious fraction for the VBMP and QBMP calculation sheets - 38 -
Appendix 7: Hydromodification
Supporting Detail Relating to Hydrologic Conditions of Concern
PRADO DAM
MYSTIC LAKE
PRADO DAM
REDLANDS
BEAUMONT
WILDOMAR
MURRIETA
CANYON
LAKE
CORONA
NORCO
CALIMESA
LAKE ELSINORE
BANNING
RIVERSIDE
PERRIS
JURUPA VALLEY
HEMET
EASTVALE
MENIFEE
SAN JACINTO
MORENO
VALLEY
DIAMOND VALLEY
LAKE
LAKE
SKINNER
LAKE
MATHEWS
CANYON
LAKE
LAKE
ELSINORE
LAKE
PERRIS
ZONE 1
ZONE 5
ZONE 3
ZONE 7
ZONE 4
ZONE 2
°
0 1 2 3 4
Miles
HCOC Applicability Map
Map Document: (M:\Mdata\10108202\RCFCWCD_Hydromodification_Large_5500.mxd.mxd - IRV) - 1/9/2012 Legend
Stream Type
Not Susceptible Stream Channels
Potentially Susceptible Stream Channels
Large River (Not Susceptible)
Santa Ana River
Adequate Sump
Watershed Areas
Not Applicable Area
Applicable Area
Applicable Area Watershed Boundaries
Flood Control and Water
Conservation District Boundary
Study Area
County Boundary
Hydromodification Susceptibility Documentation Report and Mapping Riverside County Flood Control and Water Conservation District Map 2
SITE
Unlined
Channel,
Since Lined
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+
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0 •l 1,
S)f\ / ~ ~ 's:}f_ .
r - 42" 48" • Q=65 Q=120
.,.--L---~ V
e:-a R 54" 48,,-,'{" , ~ 'I---~
15 • - .9c.lli_ ~ =Q=~7 ~ """
""---v' ------~~b=20' d=B' ss=2:1
Q=1600~
- J",
• ~ ~ = / li
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~ '
-~:~
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C ~'-.C.,, -~ • )\~1~· ·;~"J ,
~- \' ~---= ="------ .t::~ / ~ ~ ~ ~ q-, -
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1 (/;
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1"=800'
~-• ' -
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] , I I ' \ \ (
~~ L
LEGEND +~ 0 ~----+ ~ •• l••I- - - I RIVERSIDE COUNTY FLOOD CONTROL AND
WATER CONSERVATION DISTRICT
1' ~ -1----1- DRAINAGE BOUNDARY ,~/, : -~ oo -;oo
O 400
"
0 J.?oo •• .-----
)i<J.
·-~£,
----------- PROPOSED STORM DRAIN +
PROPOSED OPEN CHANNEL
EXISTING FACILITY
NOTES
1. ADOPTED IN OCTOBER 1980
__,...---
? MORENO
2. REVISION #1 IN APRIL 1991
0 lg ~ • ,,.
. ·-~
~ -, · ~ ~:- I
)~ " $ • • "
. • I _ , ,•-,:11i .. :l .. ,,
0=10
0=100
10 YEAR FLOW IN CFS 3. REVISION #2 IN PROGRESS
100 YEAR FLOW IN CFS
Copyright 2007 AirPhotoUSA~, LLC, All Rights Reserved
+
+
+
MASTER
DRAINAGE
PLAN
ADOPTED OCTOBER 1980 REVISION NO. 2 APRIL 2015
- 39 -
Appendix 8: Source Control
Pollutant Sources/Source Control Checklist
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
How to use this worksheet (also see instructions in Section G of the WQMP Template): 1.
Review Column 1 and identify which of these potential sources of stormwater pollutants apply to your site. Check each box that applies.
2. Review Column 2 and incorporate all of the corresponding applicable BMPs in your WQMP Exhibit.
3. Review Columns 3 and 4 and incorporate all of the corresponding applicable permanent controls and operational BMPs in your WQMP. Use the format shown in Table G.1on page 23 of this WQMP Template. Describe your specific BMPs in an accompanying narrative, and explain any special conditions or situations that required omitting BMPs or substituting alternative BMPs for those shown here.
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
A. On-site storm drain
inlets
Locations of inlets.
Mark all inlets with the words
“Only Rain Down the Storm Drain” or similar. Catch Basin Markers may be available from the Riverside County Flood Control and Water Conservation District, call 951.955.1200 to verify.
Maintain and periodically repaint or replace inlet markings. Provide stormwater pollution prevention information to new site owners, lessees, or operators. See applicable operational BMPs in Fact Sheet SC-44, “Drainage System Maintenance,” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com Include the following in lease agreements: “Tenant shall not allow anyone to discharge anything to storm drains or to store or deposit materials so as to create a potential discharge to storm drains.” B. Interior floor drains
and elevator shaft sump pumps
State that interior floor drains and
elevator shaft sump pumps will be plumbed to sanitary sewer. Inspect and maintain drains to prevent
blockages and overflow.
C. Interior parking
garages
State that parking garage floor
drains will be plumbed to the sanitary sewer.
Inspect and maintain drains to prevent
blockages and overflow.
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
D1. Need for future
indoor & structural pest control
Note building design features that
discourage entry of pests.
Provide Integrated Pest Management
information to owners, lessees, and operators.
D2. Landscape/
Outdoor Pesticide Use
Show locations of native trees or areas of shrubs and ground cover to be undisturbed and retained. Show self-retaining landscape areas, if any. Show stormwater treatment and hydrograph modification management BMPs. (See instructions in Chapter 3, Step 5 and guidance in Chapter 5.)
State that final landscape plans will accomplish all of the following. Preserve existing native trees, shrubs, and ground cover to the maximum extent possible. Design landscaping to minimize irrigation and runoff, to promote surface infiltration where appropriate, and to minimize the use of fertilizers and pesticides that can contribute to stormwater pollution. Where landscaped areas are used to retain or detain stormwater, specify plants that are tolerant of saturated soil conditions. Consider using pest-resistant plants, especially adjacent to hardscape. To insure successful establishment, select plants appropriate to site soils, slopes, climate, sun, wind, rain, land use, air movement, ecological consistency, and plant interactions.
Maintain landscaping using minimum or no pesticides. See applicable operational BMPs in “What you should know for…..Landscape and Gardening” at http://rcflood.org/stormwater/Error! Hyperlink reference not valid.
Provide IPM information to new owners, lessees and operators.
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
E. Pools, spas, ponds,
decorative fountains, and other water features.
Show location of water feature and
a sanitary sewer cleanout in an accessible area within 10 feet. (Exception: Public pools must be plumbed according to County Department of Environmental Health Guidelines.) If the Co-Permittee requires pools
to be plumbed to the sanitary sewer, place a note on the plans and state in the narrative that this connection will be made according to local requirements. See applicable operational BMPs in
“Guidelines for Maintaining Your Swimming Pool, Jacuzzi and Garden Fountain” at http://rcflood.org/stormwater/ F. Food service
For restaurants, grocery stores, and other food service operations, show location (indoors or in a covered area outdoors) of a floor sink or other area for cleaning floor mats, containers, and equipment. On the drawing, show a note that this drain will be connected to a grease interceptor before discharging to the sanitary sewer.
Describe the location and features of the designated cleaning area. Describe the items to be cleaned in this facility and how it has been sized to insure that the largest items can be accommodated. See the brochure, “The Food Service
Industry Best Management Practices for: Restaurants, Grocery Stores, Delicatessens and Bakeries” at http://rcflood.org/stormwater/Provide this brochure to new site owners, lessees, and operators. G. Refuse areas
Show where site refuse and recycled materials will be handled and stored for pickup. See local municipal requirements for sizes and other details of refuse areas. If dumpsters or other receptacles are outdoors, show how the designated area will be covered, graded, and paved to prevent runon and show locations of berms to prevent runoff from the area. Any drains from dumpsters, compactors, and tallow bin areas shall be connected to a grease removal device before discharge to sanitary sewer.
State how site refuse will be handled and provide supporting detail to what is shown on plans. State that signs will be posted on or near dumpsters with the words “Do not dump hazardous materials here” or similar. State how the following will be
implemented: Provide adequate number of receptacles. Inspect receptacles regularly; repair or replace leaky receptacles. Keep receptacles covered. Prohibit/prevent dumping of liquid or hazardous wastes. Post “no hazardous materials” signs. Inspect and pick up litter daily and clean up spills immediately. Keep spill control materials available on-site. See Fact Sheet SC-34, “Waste Handling and Disposal” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
H. Industrial processes.
Show process area.
If industrial processes are to be
located on site, state: “All process activities to be performed indoors. No processes to drain to exterior or to storm drain system.” See Fact Sheet SC-10, “NonStormwater Discharges” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com See the brochure “Industrial & Commercial Facilities Best Management Practices for: Industrial, Commercial Facilities” at http://rcflood.org/stormwater/
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
I. Outdoor storage of
equipment or materials. (See rows J and K for source control measures for vehicle cleaning, repair, and maintenance.)
Show any outdoor storage areas, including how materials will be covered. Show how areas will be graded and bermed to prevent runon or run-off from area. Storage of non-hazardous liquids shall be covered by a roof and/or drain to the sanitary sewer system, and be contained by berms, dikes, liners, or vaults. Storage of hazardous materials and wastes must be in compliance with the local hazardous materials ordinance and a Hazardous Materials Management Plan for the site.
Include a detailed description of
materials to be stored, storage areas, and structural features to prevent pollutants from entering storm drains. Where appropriate, reference documentation of compliance with the requirements of Hazardous Materials Programs for:
Hazardous Waste Generation
Hazardous Materials Release
Response and Inventory
California Accidental Release
(CalARP)
Aboveground Storage Tank
Uniform Fire Code Article 80
Section 103(b) & (c) 1991
Underground Storage Tank
www.cchealth.org/groups/hazmat
/
See the Fact Sheets SC-31, “Outdoor
Liquid Container Storage” and SC-33, “Outdoor Storage of Raw Materials ” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
J. Vehicle and
Equipment Cleaning
Show on drawings as appropriate:
(1) Commercial/industrial facilities having vehicle/equipment cleaning needs shall either provide a covered, bermed area for washing activities or discourage vehicle/equipment washing by removing hose bibs and installing signs prohibiting such uses. (2) Multi-dwelling complexes shall have a paved, bermed, and covered car wash area (unless car washing is prohibited on-site and hoses are provided with an automatic shutoff to discourage such use). (3) Washing areas for cars, vehicles, and equipment shall be paved, designed to prevent run-on to or runoff from the area, and plumbed to drain to the sanitary sewer. (4) Commercial car wash facilities shall be designed such that no runoff from the facility is discharged to the storm drain system. Wastewater from the facility shall discharge to the sanitary sewer, or a wastewater reclamation system shall be installed. If a car wash area is not provided,
describe any measures taken to discourage on-site car washing and explain how these will be enforced.
Describe operational measures to implement the following (if applicable): Washwater from vehicle and equipment washing operations shall not be discharged to the storm drain system. Refer to “Outdoor Cleaning Activities and Professional Mobile Service Providers” for many of the Potential Sources of Runoff Pollutants categories below. Brochure can be found at http://rcflood.org/stormwater/Car dealerships and similar may rinse cars with water only.
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
K. Vehicle/Equipment
Repair and Maintenance
Accommodate all vehicle equipment repair and maintenance indoors. Or designate an outdoor work area and design the area to prevent run-on and runoff of stormwater. Show secondary containment for exterior work areas where motor oil, brake fluid, gasoline, diesel fuel, radiator fluid, acid-containing batteries or other hazardous materials or hazardous wastes are used or stored. Drains shall not be installed within the secondary containment areas. Add a note on the plans that states either (1) there are no floor drains, or (2) floor drains are connected to wastewater pretreatment systems prior to discharge to the sanitary sewer and an industrial waste discharge permit will be obtained.
State that no vehicle repair or maintenance will be done outdoors, or else describe the required features of the outdoor work area. State that there are no floor drains or if there are floor drains, note the agency from which an industrial waste discharge permit will be obtained and that the design meets that agency’s requirements. State that there are no tanks, containers or sinks to be used for parts cleaning or rinsing or, if there are, note the agency from which an industrial waste discharge permit will be obtained and that the design meets that agency’s requirements.
In the Stormwater Control Plan, note that all of the following restrictions apply to use the site:
No person shall dispose of, nor permit the disposal, directly or indirectly of vehicle fluids, hazardous materials, or rinsewater from parts cleaning into storm drains. No vehicle fluid removal shall be performed outside a building, nor on asphalt or ground surfaces, whether inside or outside a building, except in such a manner as to ensure that any spilled fluid will be in an area of secondary containment. Leaking vehicle fluids shall be contained or drained from the vehicle immediately. No person shall leave unattended drip parts or other open containers containing vehicle fluid, unless such containers are in use or in an area of secondary containment. Refer to “Automotive Maintenance & Car Care Best Management Practices for Auto Body Shops, Auto Repair Shops, Car Dealerships, Gas Stations and Fleet Service Operations”. Brochure can be found at http://rcflood.org/stormwater/Refer to Outdoor Cleaning Activities and Professional Mobile Service Providers for many of the Potential Sources of Runoff Pollutants categories below. Brochure can be found at http://rcflood.org/stormwater/
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
L. Fuel Dispensing
Areas
Fueling areas6 shall have
impermeable floors (i.e., portland cement concrete or equivalent smooth impervious surface) that are: a) graded at the minimum slope necessary to prevent ponding; and b) separated from the rest of the site by a grade break that prevents run-on of stormwater to the maximum extent practicable. Fueling areas shall be covered by a canopy that extends a minimum of ten feet in each direction from each pump. [Alternative: The fueling area must be covered and the cover’s minimum dimensions must be equal to or greater than the area within the grade break or fuel dispensing area1.] The canopy [or cover] shall not drain onto the fueling area.
The property owner shall dry sweep the fueling area routinely. See the Fact Sheet SD-30 , “Fueling Areas” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com 6 The fueling area shall be defined as the area extending a minimum of 6.5 feet from the corner of each fuel dispenser or the length at which the hose and nozzle assembly may be operated plus a minimum of one foot, whichever is greater.
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
M. Loading Docks
Show a preliminary design for the loading dock area, including roofing and drainage. Loading docks shall be covered and/or graded to minimize run-on to and runoff from the loading area. Roof downspouts shall be positioned to direct stormwater away from the loading area. Water from loading dock areas shall be drained to the sanitary sewer, or diverted and collected for ultimate discharge to the sanitary sewer. Loading dock areas draining directly to the sanitary sewer shall be equipped with a spill control valve or equivalent device, which shall be kept closed during periods of operation. Provide a roof overhang over the loading area or install door skirts (cowling) at each bay that enclose the end of the trailer.
Move loaded and unloaded items indoors as soon as possible. See Fact Sheet SC-30, “Outdoor Loading and Unloading,” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
N. Fire Sprinkler Test
Water
Provide a means to drain fire
sprinkler test water to the sanitary sewer.
See the note in Fact Sheet SC-41,
“Building and Grounds Maintenance,” in the CASQA Stormwater Quality Handbooks at www.cabmphandbooks.com
O. Miscellaneous Drain
or Wash Water or Other Sources Boiler drain lines Condensate drain lines Rooftop equipment Drainage sumps Roofing, gutters, and trim. Other sources
Boiler drain lines shall be directly or indirectly connected to the sanitary sewer system and may not discharge to the storm drain system. Condensate drain lines may discharge to landscaped areas if the flow is small enough that runoff will not occur. Condensate drain lines may not discharge to the storm drain system. Rooftop equipment with potential to produce pollutants shall be roofed and/or have secondary containment. Any drainage sumps on-site shall feature a sediment sump to reduce the quantity of sediment in pumped water. Avoid roofing, gutters, and trim made of copper or other unprotected metals that may leach into runoff. Include controls for other sources as specified by local reviewer.
STORMWATER POLLUTANT SOURCES/SOURCE CONTROL CHECKLIST
IF THESE SOURCES WILL BE ON THE PROJECT SITE … … THEN YOUR WQMP SHOULD INCLUDE THESE SOURCE CONTROL BMPs, AS APPLICABLE 1 Potential Sources of
Runoff Pollutants
2 Permanent Controls—Show on
WQMP Drawings
3 Permanent Controls—List in WQMP
Table and Narrative
4 Operational BMPs—Include in WQMP
Table and Narrative
P. Plazas, sidewalks,
and parking lots.
Sweep plazas, sidewalks, and parking
lots regularly to prevent accumulation of litter and debris. Collect debris from pressure washing to prevent entry into the storm drain system. Collect washwater containing any cleaning agent or degreaser and discharge to the sanitary sewer not to a storm drain. - 40 -
Appendix 9: O&M
Operation and Maintenance Plan and Documentation of Finance, Maintenance and Recording Mechanisms - 6 -
Appendix 10: Educational Materials
BMP Fact Sheets, Maintenance Guidelines and Other End-User BMP Information Riverside County - Low Impact Development BMP Design Handbook rev. 2/2012