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cc 2022 AR 08/23 melrose way 15 lot subdivision p21-0130

Vista City Council
August 23, 2022

Document
cc 2022 AR 08/23 melrose way 15 lot subdivision p21-0130
Meeting
August 23, 2022
Body
Vista City Council
Pages
38
Original file
3.6 MB
Text extracted from the city's file for reading and search. Open the original on portal.laserfiche.com. That file is the official record.

1205 Melrose Way

ENGINEER OF WORK CERTIFICATION STATEMENT
Preparer's Certification
I hereby declare that I am the Engineer in Responsible Charge of design of storm water best management practices (BMPs)for this project, and that I have exercised responsible charge over the design of the BMPs as defined in Section 6703 of the Business and Professions Code, and that the design is consistent with the PDP requirements of the City of Vista BMP Design Manual,which is a design manual for compliance with local City and regional MS4 Permit(California Regional Water Quality Control Board San Diego Region Order No. R9-2015- 0100) requirements for storm water management.

I have read and understand that the City Engineer has adopted minimum requirements for managing urban runoff, including storm water,from land development activities, as described in the BMP Design Manual. I certify that this PDP SWAMP has been completed to the best of my ability and accurately reflects the project being proposed and the applicable BMPs proposed to minimize the potentially negative impacts of this project's land development activities on water quality. I understand and acknowledge that the plan check review of this PDP SWAMP by the City Engineer is confined to a review and does not relieve me, as the Engineer in Responsible Charge of design of storm water BMPs for this project, of my responsibilities for project design.

SWAMP PREPARED BY:

William J. Suiter
Pasco Laret Suiter&Associates
27127 Calle Arroyo, Suite 1904
San Juan Capistrano, CA 92675
949-661-6695
[email protected]
RCE68964
12-31-23
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Signature, PE ense Num er& Expiration Date
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William Justin uiter �`
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01/13/2022 OF CAS-
Date

Page 3 of 38 ends

1205 Melrose Way

PROJECT OWNER CERTIFICATION STATEMENT
Owners Certification
This PDP SWAMP has been prepared for Zoran Djordjevich by Pasco Laret Suiter&Associates.The PDP SWAMP is intended to comply with the PDP requirements of the City of Vista BMP Design Manual, which is a design manual for compliance with local City and regional MS4 Permit (California Regional Water Quality Control Board San Diego Region Order No. 119-2015-0100) requirements for storm water management.

The undersigned,while it owns the subject property, is responsible for the implementation of the provisions of this plan. Once the undersigned transfers its interests in the property, its successor-in-interest shall bear the aforementioned responsibility to implement the best management practices (BMPs) described within this plan, including ensuring on-going operation and maintenance of structural BMPs.A signed copy of this document shall be available on the subject property into perpetuity.

OWNER DETAILS:

Zoran Djordjevich
551 Lynwood Dr
Encinitas, CA 92024
(760)497-8761
[email protected]
Project Owner's Signature
Print Name
Date

Page 4 of 38 ends

120S Melrose Way

CITY OF VISTA STAFF REVIEW
Reviewed and Approved:

City Staff Signature: Date:

Page 5 of 38 ends

1205 Melrose Way

PAGE INTENTIONALLY BLANK

Page 6 of 38 ends

1205 Melrose Way

PROJECT VICINITY MAP
Project Name: 1205 Melrose Way
7 Permit Application Number: P21-0130
Insert Project Vicinity Map Below:

VICINITY MAP
HIGHWAY 78
SITE
w
MELROsE WAYLU
o
SUNS w o
N co
W E
S

Page 7 of 38 ends

1205 Melrose Way
FORM 1 - PROJECT CATEGORY DETERMINATION CHECKLIST
This form is used to assess stormwater BMP requirements applicable to the proposed project.The form is available as a stand-alone fillable checklist on the City's website and a completed copy must be included with the final SWAMP submitted to the City.The form is available at:
http://www.cityofvista.com/services/city-departments/community-development/building-planning- permits-applications/land-development-autocad-templates/storm-water-forms

Page 8 of 38 ends

Project ID:

CHECKLIST FOR DETERMINATION OF PROJECT
CITY OF VISTA CATEGORY
C A L I F 0 R N I A
Project Name: 1205 Melrose Way
Project Location:

APPLICABILITY OF PERMANENT, POST-CONSTRUCTION STORMWATER BMP

REQUIREMENTS AND PROJECT TYPE DETERMINATION
Overview and Instructions
The City of Vista's (City's) Stormwater Management Program is regulated by the San Diego regional municipal stormwater permit(referred to as a Municipal Separate Storm Sewer System Permit).This permit requires that new development and redevelopment projects incorporate permanent stormwater Best Management Practices (BMPs) into the project design. The City of Vista's BMP Design Manual(formerly SUSMP Manual) discusses BMP requirements applicable to new development and redevelopment projects.

ALL STANDARD AND PRIORITY PROJECTS ARE REQUIRED TO INCORPORATE SITE DESIGN AND SOURCE CONTROL BMPS. Additional treatment control and hydromodification management BMP requirements apply to projects that meet specific criteria or thresholds. This checklist must be completed by the project applicant or proponent, and is used to determine if those additional BMPs are required.

Not all site improvements are considered "development projects"under the MS4 Permit.

Development projects are defined by the MS4 Permit as "construction, rehabilitation, redevelopment, or reconstruction of any public or private projects". Development projects are issued local permits to allow construction activities. To further clarify, this checklist applies only to new development or redevelopment activities and/or projects that have the potential to contact storm water and contribute an anthropogenic source of pollutants, or reduce the natural absorption and infiltration abilities of the land.

A project must be defined consistent with the California Environmental Quality Act (CEQA) definitions of"project."
CEQA requires that the project include "the whole of the action". "Whole of the Action" means the project may not be segmented or phased into small parts either onsite or offsite if the effect is to reduce the quantity of impervious area and fall below thresholds for applicability of storm water requirements. This requirement precludes "piece-mealing," which is the improper (and often artificial) separation of a project into smaller parts to avoid preparing Environmental Impact Report level documentation.

As indicated above, for the purposes of the BMP Design Manual, the "project" is the "whole of the action" which has the potential for adding or replacing or resulting in the addition or replacement of, roofs, pavement, or other impervious surfaces, thereby resulting in increased flows and storm water pollutants.

When defining the project, the following questions are considered:
• What are the project activities?
• Do they occur onsite or offsite?
• What are the limits of the project (project boundary)? • What is the whole of the action associated with the project (i.e. what is the total amount of new or

replaced impervious area considering all of the collective project components through all phases of the project)?
• Are any facilities or agreements to build facilities offsite in conjunction with providing service to the project (street-widening, utilities)?
Responses to the checklist represent an initial assessment of the proposed project conditions and impacts.

City staff will confirm this checklist based on assessment of the development application and/or project plans. Results of the checklist will classify a project as one of the following: Priority Development Project, Standard Project, or Non-development Project.

If additional information is needed while completing this checklist, please refer to the City's BMP Design Manual. Alternatively, contact City Land Development staff.

This Form is divided into 4 sections:

1. Post-Construction Stormwater Requirement Exemptions

2. Priority Development Project Determination

3. Special Consideration for Redevelopment Projects (50 Percent Rule)

4. Final Project Determination

JECTION
• • • • ' ' City of Vista• • • This section will determine whether your project is exempt from post- construction BMP requirements and would be classified as a Non-Development YES NO Project. See section 1.3 of the City's BMP Design Manualfor further discussion. (a) Replacement of impervious surfaces that are part of a routine maintenance activity, such as (check yes if any apply): ❑ (i) Replacing roof material on an existing building
(i i) Rebuilding a structure to original design after damage from earthquake, fire or similar disaster
(iii) Restoring pavement or other surface materials affected by trenches from utility work
(iv) Resurfacing existing roads and parking lots, including slurry, overlay and restriping
(v) Routine replacement of damaged pavement, including full depth replacement, if the sole purpose is to repair the damage (vi) Constructing new sidewalk, pedestrian ramps or bike lanes on existing roads (within existing street right-of-way)
(vii) Restoring a historic building to its original historic design (viii) Routine replacement of damaged pavement, such as pothole repair
Note: Work that creates impervious surface outside of the existing impervious footprint is not considered routine maintenance.
(b) Repair or improvements to an existing building or structure that do not ❑ alter the size (check yes if any apply):
(i) Plumbing, electrical and HVAC work
(i i) Interior alterations including major interior remodels and tenant build- out within an existing commercial building
(iii) Exterior alterations that do not change the general dimensions and structural framing of the building (does not include building additions or projects where the existing building is demolished)
If you answered YES to either category (a) or (b), your project is considered a Non-Development Project, and post construction BMP requirements do not apply. Please proceed to Section 4 and check the Non- Development Project box.

If you answered NO to category (a) and (b), please proceed to Section 2.

• N 2 - PRIORITY DEVELOPMENTPROJECT City of Vista

DETERMINATION
This section determines whether your project is a Priority Development Project(PDP) or a Standard Project. See section 1.4 of the City's BMP YES NO Design Manual for further discussion. The following eight (8) types of projects are defined as PDPs:
(a) New development projects that create 10,000 square feet or more of impervious surfaces (collectively over the entire project site). This includes ® ❑ commercial, industrial, residential, mixed-use, and public development projects on public or private land.
(b) Redevelopment projects that create and/or replace 5,000 square feet or more of impervious surface (collectively over the entire project site on an existing site of 10,000 square feet or more of impervious surfaces). This ❑ includes commercial, industrial, residential, mixed-use, and public development projects on public or private land.
(c) New and redevelopment projects that create and/or replace 5,000 square feet or more of impervious surface (collectively over the entire project site), and support one or more of the following uses:
(i) Restaurants. This category is defined as a facility that sells prepared foods and drinks for consumption, including stationary lunch counters and refreshment stands selling prepared foods and drinks for immediate consumption (Standard Industrial Classification (SIC) code 5812). (ii) Hillside development projects. This category includes development on ❑ any natural slope that is twenty-five percent or greater. (iii) Parking lots. This category is defined as a land area or facility for the temporary parking or storage of motor vehicles used personally, for business, or for commerce.
(iv) Streets, roads, highways, freeways, and driveways. This category is defined as any paved impervious surface used for the transportation of automobiles, trucks, motorcycles, and other vehicles.

(d) New or redevelopment projects that create and/or replace 2,500 square feet or more of impervious surface (collectively over the entire project site), and ❑ discharge directly to an Environmentally Sensitive Area (ESA). "Discharging directly to" includes flow that is conveyed overland a distance of 200 feet or less from the project to the ESA, or conveyed in a pipe or open channel any distance as an isolated flow from the project to the ESA (i.e. not commingled with flows from adjacent lands).

Note: ESAs are areas that include but are not limited to all Clean Water Act Section 303(d) impaired water bodies; State Water Quality Protected Areas; water bodies designated with the RARE beneficial use by the State Water Board and San Diego Water Board; and any other equivalent environmentally sensitive areas which have been identified by the City.

For projects adjacent to an ESA, but not discharging to an ESA, the 2,500 sq-ft threshold does not apply as long as the project does not physically disturb the ESA and the ESA is upstream of the project.

There are no Areas of Special Biological Significance (ASBS) or State Water Quality Protected Areas in the City's jurisdiction. The ESAs within the City's boundaries which include 303(d)-listed impairments and RARE beneficial use designations are listed below:
• Agua Hedionda Creek
• Buena Creek
• Buena Vista Creek
• Loma Alta Creek
(e) New development projects, or redevelopment projects that create and/or ❑ replace 5,000 square feet or more of impervious surface, that support one or more of the following uses:
(i) Automotive repair shops. This category is defined as a facility that is categorized in any one of the following SIC codes: 5013, 5014, 5541, 7532-7534, or 7536-7539.
(i i) Retail gasoline outlets.This category includes Retail gasoline outlets that meet the following criteria: (a) 5,000 square feet or more or (b) a projected Average Daily Traffic of 100 or more vehicles per day. (f) New or redevelopment projects that result in the disturbance of one or more ® ❑ acres of land and are expected to generate pollutants post construction. This means any activity that moves soils or substantially alters the pre-existing vegetated or man-made cover of any land. This includes, but is not limited to the following:
(i) Grading, digging, cutting, scraping, stockpiling, pavement removal, and exterior construction;
(i i) Substantial removal of vegetation where soils are disturbed including but not limited to removal by clearing or grubbing; or
(iii) Any activity which bares soil or rock or involves streambed alterations or the diversion or piping of any watercourse.

If you answered YES to any of the categories above (a-f), your project is considered a PDP. Please proceed to section 3 and check the Priority Development Project Box in Section 4.

If you answer NO to all categories, then your project is considered a Standard Project. Please proceed to Section 4 and check the Standard Project Box.

This section determines additional considerations required for Redevelopment YES NO PDPs. See section 1.7 of the City's BMP Design Manual for further discussion.

Will redevelopment result in the creation or replacement of impervious surface in ❑ ❑ an amount of more than 50 percent of the surface area of the previously existing development? See clarification on calculation of the ratio of impervious surface below.

These requirements for managing storm water on an entire redevelopment project site are commonly referred to as the "50 Percent Rule". For the purpose of calculating the ratio, the surface area of the previously existing development shall be the area of impervious surface within the previously existing development. The following steps shall be followed to estimate the area that requires treatment to satisfy the MS4 Permit requirements:

1. How much total impervious area currently exists on the site?

2. How much existing impervious area will be replaced with new impervious area?

3. How much new impervious area will be created in areas that are pervious in the existing condition?

4. Total created and/or replaced impervious surface = Step 2 + Step 3.

5. 50 Percent Rule Test: Is step 4 more than 50 Percent of Step 1? If yes, treat all impervious surface on the site (including existing impervious surface not being replaced or added). If no, then treat only Step 4 impervious surface and any area that comingles with created and/or replaced impervious surface area.

Note: Step 2 and Step 3 must not overlap, as it is fundamentally not possible for a given area to be both "replaced" and "created" at the same time. Also activities that occur as routine maintenance (see Section 1 of this form) shall not be included in Step 2 and Step 3 calculation.

For example, a 10,000 square foot development proposes replacement of 4,000 square feet of impervious area. The treated area is less than 50 percent of the total development area and only the 4,000 square foot area is required to be treated.

If you answered YES, then you must implement the PDP requirements for all impervious surfaces across the entire site. Please proceed to Section 4 and check the box under PDP indicating that the Project Is a Redevelopment Project Subject to the 50 Percent Rule.

If you answered NO,then you are only required to treat impervious surfaces that are replaced or created.

Please proceed to section 4 and check the box under PDP indicating this is Not a Redevelopment Project Subject to the 50 Percent Rule.

-P City of Vista
EECTION 4 - FINAL PROJECT DETERIVIINATION�� BMP Design Manua BASED ON THE INFORMATION PROVIDED IN SECTIONS 1-3, THIS PROJECT IS DETERMINED TO BE A:
® PRIORITY DEVELOPMENT PROJECT. PRIORITY REQUIREMENTS APPLY AND A STORM

WATER QUALITY MANAGEMENT PLAN (SWQMP) MUST BE SUBMITTED AT THE TIME OF APPLICATION.
❑ THIS IS A REDEVELOPMENT PROJECT SUBJECT TO THE 50 PERCENT RULE. ❑x THIS IS NOT A REDEVELOPEMNT PROJECT SUBJECT TO THE 50 PERCENT RULE. ❑ STANDARD PROJECT. STANDARD REQUIREMENTS APPLY AND APPLICABLE SECTIONS

OF A STORM WATER QUALITY MANAGEMENT PLAN (SWQMP) MUST BE SUBMITTED AT THE TIME OF APPLICATION.
❑ NON DEVELOPMENT PROJECT.

Applicant Information and Signature Box City use only Address: APN(s) Concur: Yes No
1205 Melrose Way 166-184-09 &10, 166-183-17
Applicant Name: Applicant Title: By:

Date:

Applicant Signature: Date:

Land Dev#:

Supporting discussion for this checklist, as well as BMP requirements for Priority Development Projects and Standard Projects, is provided in the City of Vista BMP Design Manual.

1205 Melrose Way
FORM 2 - PROJECT OVERVIEW

Page 1 of 11 ends

Project Name 1205 Melrose Way
Project Address 1205 Melrose Way
Vista, CA 92081
Assessor's Parcel Number(s) (APN(s)) 166-183-17, 166-184-09 & 166-184-10 Permit Application Number P21-0130
Watershed (select one checkbox; use webpage below to determine watershed) http://www.cityofvista.com/services/city-departments/community-development/building-planning- permits-applications/land-development-autocad-templates/storm-water-forms San Luis Rey ❑ Lower San Luis Rey—Mission, 903.11 Carlsbad ❑ Loma Alta—Loma Alta, 904.10
❑ Buena Vista—El Salto,904.21
❑X Buena Vista—Vista, 904.22
❑X Agua Hedionda—Los Monos, 904.31
❑ Agua Hedionda—Buena, 904.32
❑ San Marcos—Batiquitos, 904.51
Parcel Area
(total area of Assessor's Parcel(s) associated 1 2.67 Acres (516,243 Square Feet) with the project)
Area to be Disturbed by the Project
(Project Area) 1 2.85 Acres (524,210 Square Feet) Project Proposed Impervious Area
(subset of Project Area) 1 1.36* Acres ( 59,386* Square Feet) Project Proposed Pervious Area
(subset of Project Area) 1 1•49** Acres ( 64,824** Square Feet) NOTE: Proposed Impervious Area + Proposed Pervious Area =Area to be Disturbed by the Project.

This may be less than the Parcel Area.
* 51,837 sf impervious area on-site+7,549 sf impervious area off-site = 59,386 sf total ** 59,503 sf pervious area on-site+5,321 sf pervious area off-site=64,824 sf total

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1205 Melrose Way
Form 2, Page 2 of 11

DESCRIPTION OF EXISTING SITE CONDITIONS
Current Status of the Site (select all that apply and describe below):

Z Existing development
❑ Previously graded but not built out
❑ Demolition completed without new construction
❑ Agricultural or other non-impervious use
X Vacant, undeveloped/natural
Describe:

An existing single-family home is located in the southwest corner of 166-184-10.The remaining portion of 166-184-10, all of 166-184-09 and 166-183-17 are un-developed/vacant land.

Existing Land Cover Includes (select all that apply and describe below):

Z Vegetative Cover 1 2.493 Acres ( 108,613 Square Feet) ❑ Non-Vegetated Pervious Areas I Acres ( Square Feet) 0 Impervious Areas 1 0.175 Acres( 7,630 Square Feet) Describe:

Existing single-family home is located in the southwest corner of 166-184-10 with associated hardscape.

The remaining land is un-developed/vacant.

Underlying Soil belongs to Hydrologic Soil Group (select all that apply):
❑ NRCS Type A
❑ NRCS Type B
❑ NRCS Type C
0 NRCS Type D
Approximate Depth to Groundwater(GW):
❑ GW Depth 20 feet
Per project Geotechnical Study, no groundwater was encountered during their testing.

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120S Melrose Way
Existing Natural Hydrologic Features (select all that apply and describe in next section):
❑ Drainage ditch/Swale/Waterway
❑ Seeps
❑ Springs
❑ Wetlands
0 None

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1205 Melrose Way
Form 2, Page 3 of 11

DESCRIPTION OF EXISTING SITE DRAINAGE PATTERNS
How is storm water runoff conveyed from the site?At a minimum, this description should answer:

1. Is existing site drainage conveyance natural or improved storm drain (urbanized);

2. Is runoff from offsite conveyed through the site? If yes, quantify all offsite drainage areas, design flows, and locations where offsite flows enter the project site, and summarize how such flows are conveyed through the site;

3. Provide details regarding existing project site drainage conveyance network, including any existing storm drains, concrete channels, swales, detention facilities, storm water treatment facilities, natural or constructed channels; and

4. Identify all discharge locations from the existing project site along with a summary of conveyance system size and capacity for each of the discharge locations. Provide summary of the pre-project drainage areas and design flows to each of the existing runoff discharge locations.

Describe existing site drainage patterns:

In the existing condition,the northwesterly portion of the site sheet flows southwest to northeast to a concrete ditch on the adjacent property that runs along the property line.The remaining portion of the site generally slopes from south to north toward the northeasterly corner to a concrete ditch on the adjacent property. Both ditches ultimately drain to a storm drain that flows north in existing storm drain infrastructure in Breeze Hill that flows north through the County Complex to Melrose Drive. It then flows north in Melrose Drive where it outfalls into Buena Vista Creek located north of Hacienda Drive. Buena Vista Creek outlets into Buena Vista Lagoon, and ultimately the Pacific Ocean.

Pre-project Discharge Node Area (ac) Q100 (cfs) North Basin 160 0.5 1.04
South Basin 110 2.0 3.49
Refer to the drainage report for the project titled "Hydrology Study for 1205 Melrose Way" prepared by Pasco Laret Suiter&Associates dated March 2021.

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120S Melrose Way
Form 2, Page 4 of 11

DESCRIPTION OF PROPOSED SITE DEVELOPMENT
Project Description/Proposed Land Use and/or Activities:

The project proposes to demolish the existing residence and associated hardscape improvements and construct 15 single-family detached residences, a new private street, curb &gutter, sidewalk, graded pads, drainage appurtenances, landscape, hardscape, associated utilities, and a biofiltration area designed for stormwater treatment, hydromodification management, and to mitigate for the 100-year 6-hour storm event.

Runon from the westerly adjacent properties drain onto the project site in the existing condition and will be captured in proposed brow ditches and bypass via storm drain through the project site.The storm drain will ultimately outlet to the existing brow ditches along the property boundary.

Offsite improvements to Melrose Way include removal and replacement of the half-width of asphalt, construction of curb&gutter and sidewalk along the property frontage.Additional gravel paving to be provided at the northwest corner to connect the property to the existing access drive and will be utilized for emergency vehicle access only.

Offsite improvement to the frontage on Melrose way requires additional site design BMPs to satisfy pollutant control treatment, hydromodification management, and volume retention requirements, therefore tree wells have been sized to meet the requirements.The proposed trees are located within DMA 2-1. Each tree well is a 30ft mature canopy diameter with a max soil depth of 36" and a minimum soil volume of 2cf per square foot of canopy projection for each tree, no underdrain, and provides 420 cf.Tree credit volume has been calculated per Appendix B.2.2.1 of the Storm Water Standards Manual.

Volume retention compliance has been shown using Worksheet B.5-6. Refer to Attachment 1E for all applicable completed BMP Sizing Worksheets.

List/describe proposed impervious features of the project (e.g., buildings, roadways, parking lots, courtyards, athletic courts, other impervious features):

Asphalt roadway, concrete driveways, sidewalk, and single-family residences.

List/describe proposed pervious features of the project (e.g., landscape areas):

Landscape areas and biofiltration basin.

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1205 Melrose Way
Does the project include grading and changes to site topography? ❑ Yes
❑ No
Describe:

Grading is proposed for the new access roads and pads for the homes.The project will be graded so that the site drains toward the proposed biofiltration basin.

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120S Melrose Way
Form 2, Page 5 of 11

DESCRIPTION OF PROPOSED SITE DRAINAGE PATTERNS
Does the project include changes to site drainage (e.g., installation of new storm water conveyance systems)?
❑X Yes
❑ No
If yes, provide details regarding the proposed project site drainage conveyance network, including storm drains, concrete channels, swales, detention facilities,storm water treatment facilities, natural or constructed channels, and the method for conveying offsite flows through or around the proposed project site. Identify all discharge locations from the proposed project site along with a summary of the conveyance system size and capacity for each of the discharge locations. Provide a summary of pre-and post-project drainage areas and design flows to each of the runoff discharge locations. Reference the drainage study for detailed calculations.

Describe proposed site drainage patterns:

The proposed residential lots and the proposed private streets and access roads will drain to proposed stormwater infrastructure that will outlet into the proposed biofiltration treatment basin. Stormwater will either be caught in a subdrain system, or overflow into the 36" grate inlet where it will all outlet to a proposed storm drain pipe that flows northwest to outlet into an existing concrete drainage ditch, as it does in the existing drainage condition.

A self-mitigating slope located in the northeast corner of the site will drain toward an existing concrete ditch that flows north, as it does in the in the existing drainage condition.

Off-site drainage from the west that flows on-site will be captured in proposed brow ditches and bypass via storm drain through the project site.The storm drain will ultimately outlet to the existing brow ditches along the property boundary.

Pre ProjectPost-Project
Discharge Area Q100 Discharge Area Q100 (cfs) Node ac (cfs) Node ac
North 160 0.5 1.04 175 0.05 0.10 (un-mitigated) Basin
South 110 2.0 3.49 165 2.5 3.83 (mitigated)
Basin
Offsite improvement to the frontage on Melrose way requires additional site design BMPs to satisfy pollutant control treatment, hydromodification management, and volume retention requirements, therefore tree wells have been sized to meet the requirements.The proposed trees are located within DMA 2-1. Each tree well is a 30ft mature canopy diameter with a max soil depth of 36" and a minimum soil volume of 2cf per square foot of canopy projection for each tree, no underdrain, and provides 420 cf.Tree credit volume has been calculated per Appendix B.2.2.1 of the Storm Water Standards Manual.

Volume retention compliance has been shown using Worksheet B.5-6. Refer to Attachment 1E for all applicable completed BMP Sizing Worksheets.

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1205 Melrose Way
Refer to the drainage report for the project titled "Hydrology Study for 1205 Melrose Way' prepared by Pasco Laret Suiter&Associates dated March 2021.

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1205 Melrose Way
Form 2, Page 6 of 11

POTENTIAL POLLUTANT SOURCE AREAS
Identify whether any of the following features, activities, and/or pollutant source areas will be present.

Select all Pollutant Source Areas that apply and include them on the DMA Exhibit. Source control BMPs must be identified for each of these areas in Form 3 of this SWAMP:
❑X On-site storm drain inlets
❑ Sump pumps or French drains
❑ Interior or sub-surface parking garages
❑X Need for future indoor&structural pest control
❑X Landscape/outdoor pesticide use
❑ Pools, spas, ponds, decorative fountains, or other water features ❑ Food preparation and/or service
❑X Refuse/trash collection areas
❑ Industrial processes
❑ Outdoor storage of equipment, chemicals, or materials ❑ Vehicle and equipment cleaning
❑ Vehicle/equipment repair and maintenance
❑ Fuel dispensing areas
❑ Loading docks
❑X Fire sprinkler test and relief point
❑X Miscellaneous drain or wash down areas
❑X Plazas, sidewalks, and parking lots
Describe:

Page 17 of 38 ends

120S Melrose Way
Form 2, Page 7 of 11

IDENTIFICATION AND NARRATIVE OF RECEIVING WATER AND POLLUTANTS OF CONCERN Describe flow path of storm water from the project site discharge location(s),through urban storm conveyance systems as applicable,to receiving creeks, rivers, and lagoons as applicable, and ultimate discharge to the Pacific Ocean (or bay, lagoon, lake or reservoir, as applicable):

The project site itself is located in the Agua Hedionda Hydrologic Area, however stormwater from the project drains to concrete ditches on the adjacent properties that both ultimately drain to a storm drain that flows north in existing storm drain infrastructure in Breeze Hill Rd that flows north through the County Complex to Melrose Drive. It then flows north in Melrose Drive where it outfalls into Buena Vista Creek located north of Hacienda Drive. Buena Vista Creek outlets into Buena Vista Lagoon, and ultimately the Pacific Ocean.

List any 303(d) impaired water bodies within the path of storm water from the project site to the Pacific Ocean (or bay, lagoon, lake or reservoir, as applicable), identify the poll utants)/stressor(s) causing impairment, and identify any TMDLs and/or Highest Priority Pollutants from the WQIP for the impaired water bodies:

TMDLs/WQIP Highest Priority
303(d) Impaired Water Body Pollutant(s)/Stressor(s) Pollutant Buena Vista Creek Benthic Community Effects, TMDL Required Bifenthrin, Selenium,Toxicity
Buena Vista Lagoon Indicator Bacteria, Nutrients, TMDL Required Sedimentation/Siltation,Toxicity
Identification of Project Site Pollutants*
*Identification of project site pollutants is only required if flow-thru treatment BMPs are implemented onsite in lieu of retention or biofiltration BMPs(note the project must also participate in an alternative compliance program unless prior lawful approval to meet earlier PDP requirements is demonstrated) Identify pollutants expected from the project site based on all proposed use(s) of the site (see BMP Design Manual Appendix B.6):

Not Applicable to the Expected from the Also a Receiving Water Pollutant Project Site Project Site Pollutant of Concern Sediment
Nutrients
Heavy Metals
Organic Compounds
Trash & Debris
Oxygen Demanding ❑ ❑ ❑
Substances
Oil & Grease
Bacteria &Viruses
Pesticides

Page 18 of 38 ends

1205 Melrose Way
Form 2, Page 8 of 11

HYDROMODIFICATION MANAGEMENT REQUIREMENTS
Do hydromodification management requirements apply(see Section 1.6 of the BMP Design Manual; select one box and describe below)?
❑X Yes, hydromodification management flow control structural BMPs required. ❑ No,the project will discharge runoff directly to existing underground storm drains discharging directly to water storage reservoirs, lakes, enclosed embayments, or the Pacific Ocean. ❑ No,the project will discharge runoff directly to conveyance channels whose bed and bank are concrete-lined all the way from the point of discharge to water storage reservoirs, lakes, enclosed embayments, or the Pacific Ocean.
❑ No,the project will discharge runoff directly to an area identified as appropriate for an exemption by the WMAA for the watershed in which the project resides.

Describe:

The biofiltration area designed for stormwater treatment, hydromodification management, and to mitigate for the 100-year 6-hour storm event.

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1205 Melrose Way
Form 2, Page 9 of 11

CRITICAL COARSE SEDIMENT YIELD AREAS
*This section only required if hydromodification management requirements apply Based on the maps provided within the WMAA, do potential critical coarse sediment yield areas exist within the project drainage boundaries (select all that apply and describe below)?Additional signed and stamped reports must be provided to document any exemption from coarse sediment yield requirements.
❑ Yes
❑X No, No critical coarse sediment yield areas to be protected based on WMAA maps If yes, have any of the optional analyses presented in Section 6.2 of the BMP Design Manual been performed?
❑ 6.2.1 Verification of Geomorphic Landscape Units (GLUs) Onsite ❑6.2.2 Downstream Systems Sensitivity to Coarse Sediment ❑6.2.3 Optional Additional Analysis of Potential Critical Coarse Sediment Yield Areas Onsite ❑No optional analyses performed,the project will avoid critical coarse sediment yield areas identified based on WMAA maps
If optional analyses were performed, what is the final result? ❑No critical coarse sediment yield areas to be protected based on verification of GLUs onsite ❑Critical coarse sediment yield areas exist but additional analysis has determined that protection is not required. Documentation attached in Attachment 2.13 of the SWQMP. ❑Critical coarse sediment yield areas exist and require protection.The project will implement management measures described in Sections 6.2.4 and 6.2.5 as applicable, and the areas are identified on the SWQMP Exhibit.

Describe:

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1205 Melrose Way
Form 2, Page 10 of 11

FLOW CONTROL FOR POST-PROJECT RUNOFF
*This section only required if hydromodification management requirements apply List and describe point(s) of compliance for hydromodification management flow control (see Section

6.3.1). Identify each point of compliance for flow control on the Hydromodification Management Exhibit in Attachment 2A.

There is one POC for the project, POC-1, located in the northeast corner of the project site and has a low flow threshold of 0.1Q2. Refer to the HMP exhibit located in Attachment 2a for the POC location.

Stormwater from the project drains to concrete ditches on the adjacent properties that both ultimately drain to a storm drain that flows north in existing storm drain infrastructure in Breeze Hill Rd that flows north through the County Complex to Melrose Drive. It then flows north in Melrose Drive where it outfalls into Buena Vista Creek located north of Hacienda Drive. Buena Vista Creek outlets into Buena Vista Lagoon, and ultimately the Pacific Ocean.

Has a geomorphic assessment been performed for the receiving channel(s)? ❑X No,the low flow threshold is 0.1Q2 (default low flow threshold) ❑ Yes,the result is the low flow threshold is 0.1Q2
❑ Yes,the result is the low flow threshold is 0.3Q2
❑ Yes,the result is the low flow threshold is 0.5Q2
If a geomorphic assessment has been performed, provide the report.

Discussion/Additional Information: (optional)

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1205 Melrose Way
Form 2, Page 11 of 11

OTHER SITE REQUIREMENTS AND CONSTRAINTS
When applicable, list other site requirements or constraints that will influence storm water management design, such as zoning requirements including setbacks and open space, or local codes governing minimum street width, sidewalk construction, allowable pavement types, and drainage requirements.

Optional Additional Information or Continuation of Previous Sections As Needed This space provided for additional information or continuation of information from previous sections as needed.

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1205 Melrose Way
FORM 3 - SOURCE CONTROL BMPS FOR ALL DEVELOPMENT PROJECTS

Page 1 of 4 ends

PROJECT IDENTIFICATION &SOURCE CONTROLS
Project Name: 1205 Melrose Way
Permit Application Number P21-0130
All development projects must implement source control BMPs SC-1 through SC-6, unless justification is provided by qualified design professional See Chapter 4 and Appendix E of the Model BMP Design Manual for information to implement source control BMPs shown in this checklist.

Answer each category below pursuant to the following, and provide description. • "Yes" means the project will implement the source control BMP as described in Chapter 4 and/or Appendix E of the Model BMP Design Manual.
• "No" means the BMP is applicable to the project but it is not feasible to implement. • "N/A" means the BMP is not applicable at the project site because the project does not include the feature that is addressed by the BMP (e.g.,the project has no outdoor materials storage areas).

Source Control Requirement Applied?
SC-1 Prevention of Illicit Discharges into the MS4 ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Provide effective irrigation, dispersion of non-storm water discharges into landscape SC-2 Storm Drain Stenciling or Signage I ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Site will provide prohibitive dumping placards and/or signage -Post signage at public access points to deter prohibitive dumping -Maintain legibility of placards and signage
SC-3 Protect Outdoor Materials Storage Areas from Rainfall, Run-On, ❑ Yes ❑ No ❑X N/A Runoff, and Wind Dispersal
Describe how source control will be implemented, or justify if not feasible:
-No outdoor storage areas proposed
SC-4 Protect Materials Stored in Outdoor Work Areas from Rainfall, ❑ Yes ❑ No ❑X N/A Run-On, Runoff, and Wind Dispersal
Describe how source control will be implemented, or justify if not feasible:
-No outdoor work areas proposed

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1205 Melrose Way
Form 3, Page 2 of 4
Source Control Requirement Applied?
SC-5 Protect Trash Storage Areas from Rainfall, Run-On, Runoff, and ❑X Yes ❑ No ❑ N/A Wind Dispersal
Describe how source control will be implemented, or justify if not feasible:
- Trashcans will be stored in garages
SC-6 Additional BMPs Based on Potential Sources of Runoff Pollutants Applied? (must answer for each source listed below)
a. On-site storm drain inlets ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Site will provide prohibitive dumping placards and/or signage and maintain legibility -Signage posted at public access points to deter prohibitive dumping b. Sump pumps or French drains I ❑ Yes ❑ No ❑X N/A Describe how source control will be implemented, or justify if not feasible:
-No Sump pumps or French drains proposed
c. Interior or sub-surface parking garages ❑ Yes ❑ No ❑X N/A Describe how source control will be implemented, or justify if not feasible:
-No parking garages proposed
d. Need for future indoor&structural pest control ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Provide integrated pest management information to owners, lessees and operators. e. Landscape/outdoor pesticide use ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Landscaping will be designed to minimize irrigation and runoff,to promote surface infiltration where appropriate, and to minimize the use of fertilizers and pesticides that can contribute to storm water pollution.
-BMPs will be designed with plants that are tolerant of periodic saturated soil conditions.

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1205 Melrose Way
Form 3, Page 3 of 4
Source Control Requirement Applied?
f. Pools,spas, ponds, decorative fountains, or other water features ❑ Yes ❑ No 0 N/A Describe how source control will be implemented, or justify if not feasible:
-No water features proposed
g. Food preparation and/or service ❑ Yes ❑ No 0 N/A Describe how source control will be implemented, or justify if not feasible:
-No food preparation proposed.
h. Refuse/trash collection areas ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Trash cans will be stored in proposed garages.
i. Industrial processes ❑ Yes ❑ No ❑X N/A Describe how source control will be implemented, or justify if not feasible:
-No industrial processes proposed.
j. Outdoor storage of equipment, chemicals, or materials ❑ Yes ❑ No 0 N/A Describe how source control will be implemented, or justify if not feasible:
-No outdoor storage proposed.
k. Vehicle and equipment cleaning ❑ Yes ❑ No 0 N/A Describe how source control will be implemented, or justify if not feasible:
-No vehicle cleaning proposed.

I. Vehicle/equipment repair and maintenance ❑ Yes ❑ No 0 N/A Describe how source control will be implemented, or justify if not feasible:
-No vehicle cleaning proposed.
m. Fuel dispensing areas ❑ Yes ❑ No 0 N/A Describe how source control will be implemented, or justify if not feasible:
-No fuel dispensing areas proposed

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1205 Melrose Way
Form 3, Page 4 of 4
n. Loading docks ❑ Yes ❑ No ❑X N/A Describe how source control will be implemented, or justify if not feasible:
-No loading docks proposed.
o. Fire sprinkler test water and relief point ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Drain fire sprinkler test water to the sanitary sewer. p. Miscellaneous drain or wash down areas ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Condensate drain lines and roofing to drain to landscaped areas. q. Plaza, sidewalks, parking lots ❑X Yes ❑ No ❑ N/A Describe how source control will be implemented, or justify if not feasible:
-Sidewalks and driveways to be swept. Debris from pressure washing must be collected to prevent entry into the storm drain system. Washwater containing any cleaning agent or degreaser must be collected and discharged to the sanitary sewer and not discharged to a storm drain.

Discussion/justification if SC-6 not implemented. Clearly identify which sources of runoff pollutants are discussed.Justification must be provided for all "No" answers shown above.

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1205 Melrose Way
FORM 4 - SITE DESIGN BMPS FOR ALL DEVELOPMENT PROJECTS

Page 1 of 2 ends

PROJECT IDENTIFICATION
Project Name: 1205 Merlose Way
Permit Application Number P21-0130
All development projects must implement site design BMPs SD-1 through SD-8, unless justification is provided by qualified design professional. See Chapter 4 and Appendix E of the Model BMP Design Manual for information to implement site design BMPs shown in this checklist.

Answer each category below pursuant to the following, and provide description. • "Yes" means the project will implement the site design BMP as described in Chapter 4 and/or Appendix E of the Model BMP Design Manual.
• "No" means the BMP is applicab2le to the project but it is not feasible to implement. • "N/A" means the BMP is not applicable at the project site because the project does not include the feature that is addressed by the BMP (e.g.,the project site has no existing natural areas to conserve).

Site Design Requirement Applied?
SD-1 Maintain Natural Drainage Pathways and Hydrologic Features ❑X ❑ ❑ Yes No N/A
Describe how site design will be implemented, or justify if not feasible:
-Site drainage mimics the existing condition drainage patter and discharge points.

SD-2 Conserve Natural Areas, Soils, and Vegetation I ❑ Yes ❑ No 0 N/A Describe how site design will be implemented, or justify if not feasible:

SD-3 Minimize Impervious Area I ❑X Yes ❑ No ❑ N/A Describe how site design will be implemented, or justify if not feasible:
-Streets and sidewalks designed to mimium widths, provided public safety is not compromised.

SD-4 Minimize Soil Compaction ❑ Yes ❑ No ❑X N/A Describe how site design will be implemented, or justify if not feasible:

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1205 Melrose Way
Form 4, Page 2 of 2
SD-5 Impervious Area Dispersion ❑X Yes I ❑ No ❑ N/A Describe how site design will be implemented, or justify if not feasible:
-Roof drains designed to discharge to landscape.
-Storm water biofiltration basin will effectively receive and treat runoff from impervious areas prior to discharging to the storm drain system.

SD-6 Runoff Collection ❑X Yes ❑ No ❑ N/A Describe how site design will be implemented, or justify if not feasible:
-onsite runoff will be effectively collected, conveyed and discharged via proposed storm drain.

SD-7 Landscaping with Native or Drought Tolerant Species I 0 Yes ❑ No ❑ N/A Describe how site design will be implemented, or justify if not feasible:
-Landscaping design shall consist of native and drought tolerant species.

SD-8 Harvest and Use of Precipitation ❑Yes ❑X No ❑ N/A Note: Worksheet 8.3-1, "Harvest and Use Feasibility'must be included in this section of the SWAMP.

Describe how site design will be implemented, or justify if not feasible:
-Harvesting and using precipitation is not a feasible BMP to implement. See worksheet B.3-1 in attachment 1C.

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1205 Melrose Way
FORM 5 - STRUCTURAL POLLUTANT CONTROL AND

HYDROMODIFICATION MANAGEMENT BMPS

PROJECT IDENTIFICATION
Project Name: 1205 Melrose Way
Permit Application Number P21-0130
PDP Structural BMPs
All PDPs must implement structural BMPs for storm water pollutant control (see Chapter 5 of the BMP Design Manual). Selection of PDP structural BMPs for storm water pollutant control must be based on the selection process described in Chapter S. PDPs subject to hydromodification management requirements must also implement structural BMPs for flow control for hydromodification management (see Chapter 6 of the BMP Design Manual). Both storm water pollutant control and flow control for hydromodification management can be achieved within the same structural BMP(s).

PDP structural BMPs must b27e verified by the local jurisdiction at the completion of construction.This may include requiring the project owner or project owner's representative and engineer of record to certify construction of the structural BMPs (see Section 1.12 of the BMP Design Manual). PDP structural BMPs must be maintained into perpetuity, and the local jurisdiction must confirm the maintenance (see Section 7 of the BMP Design Manual).

Use this form to provide narrative description of the general strategy for structural BMP implementation at the project site in the box below.Then complete the PDP structural BMP summary information sheet (page 3 of this form)for each structural BMP within the project (copy the BMP summary information page as many times as needed to provide summary information for each individual structural BMP).

Describe the general strategy for structural BMP implementation at the site.This information must describe how the steps for selecting and designing storm water pollutant control BMPs presented in Section 5.1 of the BMP Design Manual were followed, and the results (type of BMP selected). For projects requiring hydromodification flow control BMPs, indicate whether pollutant control and flow control BMPs are integrated or separate structures.

Note: Each structural pollutant control and hydromodification management BMP must be clearly identified on a site map (Attachment 1a), and described in supporting table (Attachment 113).

Step 1A:The DMAs draining to the structural BMPs are not self-mitigating, de-minimus, or self-retaining.

Step 16:There are no site design BMPs proposed for the project for which the runoff factor can be adjusted.

Step 2: Harvest and use is not feasible. Refer to Attachment 1c.

Step 3: Infiltration is not feasible. Refer to Attachment 1d.

Step 3C: Biofiltration BMPs have been selected and sized per the design criteria to meet both pollutant control and hydromodification management flow control requirements.

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1205 Melrose Way
FORM 6 - STORMWATER BMP MAINTENANCE MECHANISM

PROJECT IDENTIFICATION
Project Name: 1205 Melrose Way
Permit Application Number P21-0130
Maintenance Requirements
A stormwater structural BMP operations and maintenance plan must be prepared for PDPs. A template plan is available at:
http://www.citvofvista.com/services/city-departments/community-development/building-planning- permits-applications/land-development-autocad-templates/storm-water-forms Has a stormwater structural BMP operations and maintenance plan been prepared? ❑M Yes, included with Attachment 3A
❑ No
All projects are required to maintain designed functionality of structural BMPs in perpetuity. Privately- owned projects must record a Storm Drain Maintenance Agreement with the County of San Diego Assessor's Office. A template Storm Drain Maintenance Agreement is available at:
http://www.citVofvista.com/services/city-departments/community-development/building-planning- permits-applications/land-development-autocad-templates/storm-water-forms Has a Storm Drain Maintenance Agreement been submitted to the County? ❑ Yes, copy included with Attachment 3B
❑X No
❑ Not Applicable (e.g., city-owned property/project)

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1205 Melrose Way
ATTACHMENT 1 - POLLUTANT CONTROLS: SUPPORT DOCUMENT AND

CHECKLIST
Each of the attachments indicated below should be considered for inclusion with the SWAMP. Use this checklist to indicate which attachments are included behind this coversheet.

Attachment Contents Checklist
Sequence
Attachment 1A Drainage Management Area (DMA) ❑X Included Exhibit
See DMA Exhibit Checklist on next page.

Attachment 1B Tabular Summary of DMAs Showing ❑X Included on DMA Exhibit in Attachment 1A DMA ID matching DMA Exhibit, DMA
Area, DMA Type, and BMPs*
❑ Included as Attachment 1B
*Provide table in this Attachment OR on
DMA Exhibit in Attachment 1A
Attachment 1C Harvest and Use Feasibility Screening ❑X Included Checklist (Worksheet B.3-1)
❑ Not included because the entire project
Refer to Appendix B.3-1 of the BMP will use Infiltration BMPs Design Manual.

Attachment 1D Categorization of Infiltration Feasibility ❑X Included Condition (Worksheet C.4-1)
❑ Not included because the entire project
Refer to Appendices C and D of the BMP will use Harvest and Use BMPs Design Manual.

Attachment 1E Pollutant Control BMP Design ❑X Included Worksheets and Calculations
Refer to Appendices B and E of the BMP
Design Manual for structural pollutant
control BMP design guidelines

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1205 Melrose Way
ATTACHMENT 1A - DMA EXHIBIT CHECKLIST
For Attachment 1A, provide map(s)for the project site,titled "DMA Exhibit."The checklist below identifies minimum elements that must be included with the DMA Exhibit. ❑ Underlying hydrologic soil group
❑ Approximate depth to groundwater
❑ Existing natural hydrologic features (watercourses, seeps, springs,wetlands, etc.) ❑ Critical coarse sediment yield areas to be protected
❑ Existing topography and impervious areas
❑ Existing and proposed site drainage network and storm drain structures ❑ Proposed connections to offsite drainage
❑ Proposed demolition
❑ Proposed grading
❑ Proposed impervious features
❑ Proposed design features and surface treatments used to minimize imperviousness ❑ Drainage management area (DMA) boundaries
❑ DMA identification numbers (DMA ID)
❑ DMA areas (square footage or acreage)
❑ DMA type (Drains to BMP, Self-mitigating, De Minimis, or Self-retaining) ❑ Potential pollutant source areas and corresponding required source controls (see Form 2 and Form 3 of SWAMP, BMP Design Manual Chapter 4 and Appendix E.1) ❑ Proposed Structural BMPs (see Form 5 of SWAMP)

Page 32 of 38 ends

TG PER PLAN FREEBOARD
DEN
BRUg1 SEE TABLE HEREON I
L 3 PVC SCREW CAP 6 WSE � / 3636 BROOKS BOX i T I3657 `` ` t l / _ � _� - - ,, / / I III = -_ - ABOVE GRADE CONIC
I / " �` - �- f - « -III-III-III- - CARER PANSA PLANTING, 3705 � (� 364.E �-- � �S CONC 4 x / «IOLA� I II 1111 DENSE ��_ - III _ OR APPROVED OTHER, 6 WEIR c� ----------------------- o / I I /� TREES / _ I III - - -t=3 9 -� '�_ - I -III-III- ?1 PER LANDSCAPE PLANS Q z 5o O CON
.y D NSE / s _
I . 7 / � �3666 /3�6 /3636 ;I "� ) 1 B USH„ 1 � ` ` 2:1 (SELF-MITIGATING 4 w =� �- � o z I r EXISTING ACC�C S VE -�, �� - - - "I� I =III=I - FIG PER PLAN 2.5' INLET 12"WEIR p w w /\//\�/ / / / I II1,755 SF _ ' WEIR NOTCH PONDING LU _ /\/\\%\\%
I - - - - - - - - - - - -„--�,--r, ,->� - - _ '/ � 1 I \` \\ III I- ��J EXTEND AND WRAP LINER 12" MIN. -III=III_ -- �/\//\////\\/ I I �94// 1361 III -III-I I 1=1 I 1=1 I 1=III-III-III III-III-III III-III-III -I Imo\ \\ ENGINEERED FILL LAYER SHALL BE I I / I 1 \- �\ III I r PAST EDGE OFBERM -III-III-III-III-III-III-I °° -III-III-III-III-III-I =� / MINIMUM 18" DEEP"SANDY LOAM" SOIL 370.5 x / I 365.6 / / 3626
I � �O6 \, I ► I " ,-I III-I�I-III-III-III-III III-III-I I III-III-III I I-I I I I I \ / / I I x / I \ II III I = MIX WITH NO MORE THAN 5% CLAY I 1 3665 ( 3636 I \ 36,5 I I TDENSE REES I - III-III-III-III-III-I I-III-III- -III-III-I - , CONTENT. PERCOLATION RATE I I 37L6 / I I x x I I, Q N BACKFILL IN BASIN,AND TO 5' OUTSIDE -I I I I -I I I-I I I-III-III-III III-III-III III-III-III I- \\/\\ I I 3696� / I O 1 °°NC , �34N4C _ 5-101N/HR MINIMUM.

I I / I - III I: Q I( II JIJI- I 347. SHALL CONSIST OF A 2-SACK MIX OF =1 1=1 1=1 1=1 =I =I�=I I I=I =I I =I I =I \ / I , s > l / I3656 I W \ I","I III s > 348f L LI L _ /\ n I I I ,: / I 3625 I , \_ J_35R5 _ w Il r r a a v`r _ IIJII JI4Z9 0 34.6 SLURRY -III=I \\/ 3 NON PERFORATED rIL I I / STANDPIPE 364.E I I D 3676 13 _ o �I I ~~ L - - ~I 'I - ____ ---- BOTTOM AND SIDES OF FLOW THROUGH PLANTER SHALL BE -I I \\\ a I ~ CONC , ' ' ' ' `M1 3464 -348- a- FLU 3665 / I Q I- - \ f Ilal ENSE ~ - ~"I r I x 35 34 ASPH - - _ LINED WITH 30 MIL PVC MEMBRANE THAT IS COVERED BY A _I I - - PERMAVOID LAYER ASPH MINIMUM OF 12 INCHES OF CLEAN SOIL, FREE FROM ROCKS I- Ix5 "' r 1 I I \\` ` ` ` -` 6J - AND DEBRIS,WITH A MAXIUM 3:1WITH A MAXIMUM 3:1 -III=III= QJG / /� \/\/\ WATER TIGHT CAP ON ,� � �- x '�\\ a,as .�x.B -#`��o= - - - - - - -=COND=== -III-I I / / / / \i\\/\\/\\/\ \\/\\/\\/\\/\� . �J- HORIZONTAL:VERTICAL[H:V]) SLOPE INCLINATION, ORTERMINAL END OF PIPE � , ` , SELF-MITIGATING (
aR� \ , \ DENSE - ^ FLATTER,AND MEETS THE FOLLOWING MINIMUM / FLOW CONTROL ORIFICE 6" DIAMETER PERFORATION PVC I I / 1 \ _TREES _ _ - 3 9 SF 3624 I \ I s \� _ _____ - ___ i_ SPECIFICATIONS: o PLATE PER DETAIL SUBDRAIN SHALL BE ENCAPSULATED IN - l - - -- - - ��- - -1- - - 9'G GRAVEL. GRAVEL AND SUBDRAIN SHALL °"°°g°"- SPECIFIC GRAVITY(ASTM D792): 1.2(G/CC, MIN.);TENSILE -�
- - - -- - BASIN WITH - �+�-��- OUTFACE PIPE BE WRAPPED IN MIRAFI 140N OR EQUAL. ��4 -1, � � (ASTM D882): 73 (LB/IN WIDTH, MIN); ELONGATION AT BREAK CONNECTION TO CATCH \ ' 361`. LOT A \ \ " 3sR \ (ASTM D882 380 %, MIN MODULUS ASTM D882 30 MIRAFI 140N OR EQUAL 2 DENSE � \ )� ( ), ( )• DRILLED ORFICE PLATE / / \ r \ (LB/IN-WIDTH, MIN.);AND TEAR STRENGTH (ASTM D1004): 8 (NON-WOVEN GEOTEXTILE) TREES "NOTE:(LB/IN, MIN); SEAM SHEAR STRENGTH (ASTM D882)58.4(LB/IN, **NOTE: BACKFILL FOR STORM DRAIN PIPES ENTERING OR EXISTING \ FIG 357.6 MIN); SEAM PEEL STRENGTH (ASTM D882) 15 (LB/IN, MIN). BASIN SHOULD BE BACKFILLED WITH A 2-SACK MIX OF SLURRY DENSE
BRUSH ,�.� r r = ` ` ` ` \ 360 �,300 SF � \ a PROVIDE 18-INCH OVERLAPPED,TAPED OR MIN 6 3 \\ `` = r = ° ` ` GLUED SEAMS AT ALL SEAMS. PLACE 3„ l ORFICE PLATE MIN. SQUARE DIMENSIONS 1.0 FT \ I \ 352.5 NON-WOVEN FILTER FABRIC(MIRAFI 140N OR 1 GREATER THAN PIPE DIA. HOT-DIP GALVANIZED 3 \" 3535 \ASPH x EQUAL) ON EITHER SIDE OF PVC LINER TO PROTECT LINER PLATE AFTER HOLES HAVE BEEN DRILLED FROM PUNCTURE ON ALL SIDES, "SANDWHICHING"THE PVC INFLOW PIPE } LINER WITH A FABRIC CUSHION.
364.7 \ \ I'' \ 36 I I \ \ SELF-MITIGATING ~ \� 359.E I \ \ x5 « SIZE OF DRILLED ORFICE PER 2,054 SIF ~ I \ t 45 BIOFILTRATION BASIN TABLE o s / , � _ 112" MAX DENSE I I 3636 I \ ~" \ DMA 1- ° " TABLE HEREON / BRUSH I I � = BASIN NO. ENGINEERED PERMAVOID TOTAL FREE ORIFICE / s r r r t a \ t t BRUSH3555 „ 3653 5 « = SOIL LAYER LAYER PONDING BOARD355 3l8" DIA. HOLE I1 TDENSEREES O4 \ ~ y �«� = 1 18" 38.4" 12" 1.0' 1.5" FLOW CONTROL ORFICE PLATE 367.6 c
\ 3645 _
- BIOFILTRATION BASIN DETAIL
BRUSH DENSE " 3�=
TREES 35F 5 3573�
365.E I / « "
3677 N.T.S.

L
362.7 \
\ \ 364.5 Ir \ -� , DMA DATA TABLE I \ BRUSH \ � \ - DMA NO. IMPERVIOUS PERVIOUS TOTAL \ 3666 ) 3656 - / \ \ O \ ` - AREA(S.F.) AREA(S.F.) AREA(S.F.) / DENSE ~
359.J r-
t 368.7 \ \ l ,", ~ \ 36x` I I , , s , 369.3 'Q \ 367�.6 I 1 TREES y I \ 3684 \ \ s s , , , , , ` � ~ w 1-1 53,174 52,620 105,794 LU
\ \�\ - 365- \ N 360.5 2-1 5,171 537 5,708 ASPH
�16. 4 (~/) - - SELF-
.. . . . . 361.5
I t r r r \ ----- -----� r-� U I - �� MITIGATING 4,188SF BMP NOTES II \^ -
3695 l / 36� \ \\ I I Z \ ROCKS M` ` ` Q 0 I DE-MINIMUS 275 SF 1. THESE BMPS AREA MANDATORY TO BE INSTALLED PER MANUFACTURER'S _ _.3 CONC 3696 \ 3676 I ^^ I 364.4 \\ -36¢- 3636 BRUSH M / L AREA RECOMMENDATIONS OR THERE PLANS I I 3695 x II \ x \ 366.4 \ � '}_ .

LO ' I I INFEASIBLE 2. NO CHANGES TO THE PROPOSED BMPS ON THIS SHEET WITHOUT PRIOR APPROVAL 6%.4 ` _ ` C'�'D 9 , 9 'r~ I TO ----- ----- 2,346 SF FORM THE CITY ENGINEERING DEPARTMENT 6 1 , r I I TREAT 3. NO SUBSTITUTIONS TO THE MATERIAL TYPES OR PLANTING TYPES WITHOUT PRIOR BRUSH APPROVAL FROM THE LAND DEVELOPMENT ENGINEER 3646 36 I I I 4. NO OCCUPANCY WILL BE GRANTED UNTIL THE CITY INSPECTOR STAFF HAS I I p J \\ \ 3676 """ \\ \� INSPECTED THIS PROJECT FOR APPRORIATE BMP CONSTRUCTION AND I370.E I « p IT ' = '�' x � �, 5 36s546 I I GENERAL INFORMATION INSTALLATION. 3694 \"� \ , ' ' ' ' \ ', , ' • ',, , , , _ ° ' 1 I I I PROJECT SITE IS LOCATED IN THE LOS MONOS H.S.A. (904.31)OF I 3704 \ _ \ « O ~ I I 3646 AGUA HEDIONDA CREEK H.A. OF CARLSBAD H.U., HOWEVER WATER QUALITY TECHNICAL REPOT I \ , " 3656 - - Z - J I DRAINAGE FROM THE SITE ULTIMATELY DISCHARGES TO THE I I 37�'4 \\ 3704 •` " \- � 368.5 , '^ x = I o © 3647 RECIEVING WATERS OF BUENA VISTA CREEK H.S.A. (904.22)OF TITLE PRIORITY DEVELOPMENT PROJECT STORM WATER QUALITY I « Y I{1\ BUENA VISTA CREEK H.A. OF CARLSBAD H.U. 3687 H � � Y \ a r r a t x , , � \- - - - _ � w --- - - - - I MANAGEMENT REPORT FOR 1205 MELROSE WAY B I DATE-MARCH 2021
- :5 064 I POLUTTANTS OF CONCERN-BENTHIC COMMUNITY EFFECTS, 4 O� q I I -I PREPARED BY-PASCO LARET SUITER&ASSOCIATES

BIFENTHRIN, SELENIUM, TOXICITY, INDICATOR BACTERIA,
I3:/4 371.8 \ I ;- \ \}��� ' ' ' ' ' ' ' ' ' _ \ _ " I�i NUTRIENTS,AND SEDIMENTATION/SILTATION 3 z26 \ I x 377.5 \ t` r JT..6 s \ J - �372.3 \ \ slat , x ` 37Q8 -- 5- I M 4` 49 101 MAINTENANCE AGREEMENT DOCUMENT 3732
- 3726 q t ~" , \\1 I37RB I DECK 36:3 � I LID SITE DESIGN BMP'S 3703
x 3705 \ - -�L � I \`" �365f -r I TITLE- \ DECK POOL 3 - 1 y\ �" x r II I 1. BIOFILTRATION BASIN DATE- 725I/ r ' ' I L L, I I v/ I I , , III PREPARED BY- I \ �x I/ J73.5 I l o l 13709 I I / -r 1 1 "" I (/ « II 3735 , J x I �J Ihhhh' I I I^^" / 37f.3 CONp 2. ROOF DRAIN TO LANDSCAPING x -DECK 3. MINIMIZE IMPERVIOUS SURFACES -a � -comic L ._ I I �- _ _ I�� � I _ _ � OPERATIONS AND MAINTENANCE PLAN �f 370.5 \
I \ 370.9 I
/ I I « t r�CON�
o - -� 37x5 1 �a~ , , , > , , , I I I \ r - 1 ,�h , , 4. PROTECT SLOPES AND CHANNELS Q " 3743 �'r \ 9--i -'-'' /�^ - I 369.3\«,- I .85 « r I r , > TITLE-STORM WATER OPERATIONS& MAINTENANCE PLAN FOR 1205 MELROSE WAY o I - r alsJt 374.E x o C-NC- I I I « ~ I j3649 DATE-MARCH 2O21 AS I x 5. TREE WELLS
x 374.s I ` - D 14 I I I V /I z 364B I PREPARED BY-PASCO LARET SUITER&ASSOCIATES 3755 � x
Cl) S6� d37.8 La � DENSER I^\EE �� � 2= .51 �st� SOURCE CONTROL BMP'S L - - ' � _ DES \ �� ` I 364B r � RESPONSIBLE PARTY INFORMATION x - \ 375..6 " �� , , , TREE WELL#1fV52 I ASP" ":' 376.5it` " f�, > �o =� ` ` /AREA 275 SF I� 1. STORM DRAIN STENCILING w _ I"-
6 3767 DE-MINIMIS 3642 . ZORAN DJORDJEVICH I J76.7
x 3764 ELROSE qY `�\ 3727 , 'r r ` a r a r ` a r ,` ` 2. EMPLOY INTEGRATED PEST MANAGEMENT PRACTICES d 378..5 376.8 �- x 375.7 x " ' - r a - 4 i _ _ ° ` _ 551 LYNWOOD DRIVE SIGN 0 • -� 374.4 / 3734 \ l /P`` 6 \ / 6 " 4 i CONC 375..7 \ - �� 37,.7 / / 2,346 SF / _ _ SOIL INFORMATION LEGEND
x 3646 J 3638
-
�� a ^ \ -2 3636 -�- w ', N ` - - - ��_ - �M- -_ 44 CNC _ DESCRIPTION SYMBOL o HYDROLOGIC SOIL GROUP:TYPE D LOT NUMBER 10
co
CIO
m
POST-CONSTRUCTION PERMANENT BMP OPERATION GROUND WATER INFORMATION DRAINAGE DIRECTION & MAINTENANCE PROCEDURE DETAILS
GROUND WATER WAS NOT ENCOUNTERED AT THE SITE. SEE DRAINAGE MANAGEMENT AREA g 0 40 80 120 REPORT PREPARED BY: GEOSOILS, INC Li STORM WATER MANAGEMENT AND DISCHARGE CONTROL MAINTENANCE DATED: MARCH 5, 2021 W.O. 8058-A-SC TYPE-B CURB INLET Z AGREEMENT APPROVAL NO: BROOKS BOX ❑ SCALE: 1" =40' 0&M RESPONSBILE PARTY DESIGNEE: PACIFIC INTERNATIONAL INVESTMENTS, INC N HORIZONTAL DATUM: NAD 83 COARSE SEDIMENT YIELD RIP RAP BMP ID# BMP TYPE SYMBOL QUANTITY DETAIL PLAN DETAIL CONSTRUCTION BMP DESCRIPTION INSPECTION MAINTENANCE MAINTENANCE METHOD QUANTITY SHEET SET SHEET NO. NO. NORTHING FASTING CONFIRMATION FREQUENCY FREQUENCY NUMBER(S) w 30 REFER TO SEDIMENT MENTYIELD A A THIS REPORT FOR CRITICAL PASCO CARET SUITER � O LAONDSDRAIN
INGO PAD)(TWO
PER EDUCATION PROGRAM (SOURCE CONTROL) ANNUAL AS NEEDED EMPLOYEE EDUCATION PROGRAM N/A N/A COARSE SEDIMENT YIELD AREAS WITHIN THIS PROJECT SITE. DMA EXHIBIT 0 a O BIOFILTRATION 1 SIGNAGE &STENCILING ANNUAL AS NEEDED REPAIR AND/OR REPLACE AS 3 N/A 1205 MELROSE WAY o ASSG ATES N AREA
NECESSARY VISTA, CA
STORM DRAIN MOWING AND DEBRIS COLLECTION San Diego I Solana Beach I Orange County CD O STENCILING • 3 BIOFILTRATION BASIN ANNUAL AS NEEDED AS NECESSARY. REPAIR AS NEEDED 1 N/A SCALE: 1'=40' Phone 858.259.82121 www. isaen ineerin com CD DATE:AUGUST 2021 P g g• 0 Fo
TREE WELL 2 TREE WELL MONTHLY AS NEEDED INSPECT TREE HEALTH& 2 N/A SHEET 1 OF 1

REPAIR/REPLACE AS NECCESSARY

ATTACHMENT 1c

Harvest and Use Feasibility Checklist 1205 Melrose Way Harvest and Use Feasibility S

1.Is there a demand for harvested water((check all that apply) at the project site that is reliably present during the wet season?
v Toilet and urinal flushing
� Landscape irrigation
Other:

2. If there is a demand; estimate the anticipated average wet season demand over a period of 36 hours.

Guidance for planning level demand calculations for toilet/urinal flushing and landscape irrigation is provided in Section B.3.2.

Toilet/Urinal Flushing
(9.3 gal/person-day)x(0.13368 cuft/gal)x(1.5 days) = 1.86 cuft/person-36hr Assume (3 people per house x 15 houses)x(1.86 cuft/person-36 hr)=84 cuft/36hr Landscape Irrigation
(1.37 ac irrigated)x(1470 gal/ac-36hr)x(0.13368 cuft/gal) =270 cuft/36hr Total=84 cuft+270 cuft= 354 cuft

3. Calculate the DCV using worksheet B-2.1.

DCV=3,404 cult
3a. Is the 36-hour demand greater than 3b. Is the 36-hour demand greater than 3c.Is the 36-hour demand less or equal to the DCV? 0.25DCV but less than the full DCV? than 0.25DCV? Yes / d No Yes / d No v Yes Harvest and use appears to be feasible. Harvest and use may be feasible. Conduct V Harvest and use is Conduct more detailed evaluation and more detailed evaluation and sizing considered to be infeasible. sizing calculations to confirm that DCV calculations to determine feasibility. Harvest can be used at an adequate rate to meet and use may only be able to be used for a drawdown criteria. portion of the site,or(optionally) the storage may need to be upsized to meet long term
capture targets while draining in longer than
36 hours.

ATTACHMENT 1d

Appendix C: Geotechnical and Groundwater Investigation requirements Worksheet C.4-1: Categorization of Infiltration Feasibility Condition Categorization of Infiltration1 1 1 1 1 Part 1-Full Infiltration Feasibility Screening Criteria Would infiltration of the full design volume be feasible from a physical perspective without any undesirable consequences that cannot be reasonably mitigated?
Criteria Screening Question Yes No
Is the estimated reliable infiltration rate below proposed facility locations 1 greater than 0.5 inches per hour?The response to this Screening Question must X be based on a comprehensive evaluation of the factors presented in Appendix C.2 and Appendix D.

Provide basis: The USDA indicates that the site is underlain by Bosanko Clay(BsD)and Placentia sandy loam (PeC2),which are noted to have infiltration rates varying from 0.00 to 0.06 inches/hour,and is categorized as Hydrologic Soil Group"D". Furthermore,a reasonable design infiltration rate(without application of correction/ safety factors)of 0.025 inches/hour is indicated for Hydrologic Soil Group"D"soils,which is less than 0.50 inches/hour.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

Can infiltration greater than 0.5 inches per hour be allowed without increasing risk of geotechnical hazards(slope stability,groundwater mounding,utilities, 2 or other factors)that cannot be mitigated to an acceptable level? The response X to this Screening Question shall be based on a comprehensive evaluation of the factors presented in Appendix C.2.

Provide basis: Given the fact that dense bedrock exists at relatively shallow depth at the site,storm water infiltration has the potential to create perched groundwater conditions that would migrate laterally,adversely affecting both onsite and offsite improvements,including underground utilities,and even slope stability.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

I-3 February 26,2016

Appendix C: Geotechnical and Groundwater Investigation requirements Worksheet C.4-1: Categorization of Infiltration Feasibility Condition Criteria Screening Question Yes No
Can infiltration greater than 0.5 inches per hour be allowed without increasing risk of groundwater contamination(shallow water table,storm water 3 pollutants or other factors)that cannot be mitigated to an acceptable level? X The response to this Screening Question shall be based on a comprehensible evaluation of the factors presented in Appendix C.3.

Provide basis: Storm water infiltration could lead to perched groundwater conditions but measures can be incorporated into the proposed project for mitigation. Storm water pollutants such as leaking automotive fluids and brake dust are possible,however,subsurface exploration shows more than 10 feet of vertical separation between the infiltration surface elevation and the current groundwater table. Thus,there is low potential that storm water pollutants could impact groundwater quality.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

Can infiltration greater than 0.5 inches per hour be allowed without causing potential water balance issues such as a change of seasonality of ephemeral 4 streams or increased discharge of contaminated groundwater to surface X waters? The response to this Screening Question shall be based on a comprehensive evaluation of the factors presented in Appendix C.3.

Provide basis: The site is not located near a drainage course. Based on our geotechnical site exploration, groundwater appears to be greater than 50 feet below existing site grades,and likely at much lower elevations near sea level.Downstream water rights are considered a legal matter and typically do not fall within the purview of geotechnical engineering. However,GSI is not aware of any significant downstream water rights issues of concern on the adjoining properties. Given the slow soil infiltration rates onsite,infiltration should not significantly affect downstream water rights,from a geotechnical perspective.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

Part 1 In the answers to rows 1-4 are"Yes"a full infiltration design is potentially feasible. The feasibility Result* screening category is Full Infiltration
If any answer from row 1-4 is"No",infiltration may be possible to some extent but would not X Y generally be feasible or desirable to achieve a"full infiltration"design.

Proceed to Part 2
*To be completed using gathered site information and best professional judgement considering the definition of MEP in the MS4 Permit. Additional testing and/or studies may be required by Agency/Jurisdictions to substantiate findings.

I-4 February 26,2016

Appendix C: Geotechnical and Groundwater Investigation requirements Worksheet C.4-1: Categorization of Infiltration Feasibility Condition Part 2- Partial Infiltration vs. No Infiltration Feasibility Screening Criteria Would infiltration of water in an appreciable amount be physically feasible without any negative consequences that cannot be reasonably mitigated?
Criteria Screening Question Yes No
Do soil and geologic conditions allow for infiltration in any appreciable 5 rate or volume? The response to this Screening Question shall be based X on a comprehensive evaluation of the factors presented in Appendix C.2 and Appendix D.

Provide basis: The USDA indicates that the site is underlain by Bosanko Clay(BsD)and Placentia sandy loam (PeC2),which are noted to have infiltration rates varying from 0.00 to 0.06 inches/hour,and is categorized as Hydrologic Soil Group"D". Furthermore,a reasonable design infiltration rate(without application of correction/ safety factors)of 0.025 inches/hour is indicated for Hydrologic Soil Group"D"soils,which is less than 0.50 inches/hour.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

Can infiltration in any appreciable quantity be allowed without increasing risk of geotechnical hazards(slope stability,groundwater 6 mounding,utilities,or other factors)that cannot be mitigated to an X acceptable level? The response to this Screening Question shall be based on a comprehensive evaluation of the factors presented in Appendix C.2.

Provide basis: Given the fact that dense bedrock exists at relatively shallow depth at the site,storm water infiltration has the potential to create perched groundwater conditions that would migrate laterally,adversely affecting both onsite and offsite improvements,including underground utilities,and even slope stability.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

I-5 February 26,2016

Appendix C: Geotechnical and Groundwater Investigation requirements Worksheet C.4-1: Categorization of Infiltration Feasibility Condition Criteria Screening Question Yes No
Can Infiltration in any appreciable quantity be allowed without posing significant risk for groundwater related concerns (shallow water table, 7 storm water pollutants or other factors)? The response to this Screening X Question shall be based on a comprehensive evaluation of the factors presented in Appendix C.3.

Provide basis: Storm water infiltration could lead to perched groundwater conditions but measures can be incorporated into the proposed project for mitigation. Storm water pollutants such as leaking automotive fluids and brake dust are possible,however,subsurface exploration shows more than 10 feet of vertical separation between the infiltration surface elevation and the current groundwater table. Thus,there is low potential that storm water pollutants could impact groundwater quality.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

Can infiltration be allowed without violating downstream water rights? 8 The response to this Screening Question shall be based on a comprehensive X evaluation of the factors presented in Appendix C.3.

Provide basis: The site is not located near a drainage course. Based on our geotechnical site exploration, groundwater appears to be greater than 50 feet below existing site grades,and likely at much lower elevations near sea level.Downstream water rights are considered a legal matter and typically do not fall within the purview of geotechnical engineering. However,GSI is not aware of any significant downstream water rights issues of concern on the adjoining properties. Given the slow soil infiltration rates onsite,infiltration should not significantly affect downstream water rights,from a geotechnical perspective.

Summarize findings of studies;provide reference to studies,calculations,maps,data sources,etc. Provide narrative discussion of study/data source applicability.

Part 2 If all answers from row 5-8 are yes then partial infiltration design is potentially feasible.

Result* The feasibility screening category is Partial Infiltration. �j If any answer from row 5-8 is no,then infiltration of any volume is considered to be X 1 infeasible within the drainage area. The feasibility screening category is No Infiltration.
*To be completed using gathered site information and best professional judgement considering the definition of MEP in the MS4 Permit. Additional testing and/or studies may be required by Agency/Jurisdictions to substantiate findings.

I-6 February 26,2016

ATTACHMENT 1e

Appendix B: Stormwater Pollutant Control Hydrologic Calculations and Sizing Methods Worksheet B.2-1. DCV
DMA 1-1
Design Capture Volume Worksheet B-2.1
1 85th percentile 24-hr storm depth from Figure B.1-1 d= 0.65 inches 2 Area tributary to BMP (s) A= 2.43 acres Area weighted runoff factor (estimate using Appendix B.1.1 and B.2.1) 3 * See calculation below C= 0.59 unitless 4 Street trees volume reduction TCV= 0 cubic-feet 5 Rain barrels volume reduction (1 cubic foot=7.48 gallons) RCV= 0 cubic-feet Calculate DCV =
6 (3630 x C x d x A) —TCV- RCV DCV= 3404 cubic-feet Area (sq ft) Runoff Factor A x RF Weighted RF
Impervious 51837 0.9 46653
Landscape 53957 0.3 16187
Pavers 0 0.1 0
Total 105794 62840 0.59
DMA 2-1 - Tree Well#1
Design Capture Volume I a Worksheet B-2.1
1 85th percentile 24-hr storm depth from Figure B.1-1 d= 0.65 inches 2 Area tributary to BMP (s) A= 0.07 acres Area weighted runoff factor (estimate using Appendix B.1.1 and B.2.1) 3 * See calculation below = 0.84 unitless 4 Street trees volume reduction TCV= 0 cubic-feet 5 Rain barrels volume reduction (1 cubic foot=7.48 gallons) RCV= 0 cubic-feet Calculate DCV =
6 (3630 x C x d x A) —TCV- RCV DCV= 133 cubic-feet Area (sq ft) Runoff Factor A x RF Weighted RF
Impervious 2636 0.9 2372
Landscape 274 0.3 82
Pavers 0 0.1 0
Total 2910 2455 0.84
HMP Tree Well Multiplier per County BMPDM (D soil, 36" soil depth) 3.17 DCV x Tree Well Multiplier 421 cf
30-ft Diameter Mature Canopy Tree provides 420 cf DMA 2-1 - Tree Well#2
Design Capture Volume M kWorksheet B-2.1
1 85th percentile 24-hr storm depth from Figure B.1-1 d- 0.65 inches 2 Area tributary to BMP (s) A= 0.06 acres Area weighted runoff factor (estimate using Appendix B.1.1 and B.2.1) 3 * See calculation below C= 0.84 unitless 4 Street trees volume reduction TCV= 0 cubic-feet 5 Rain barrels volume reduction (1 cubic foot=7.48 gallons) RCV= 0 cubic-feet Calculate DCV =
6 (3630 x C x d x A) —TCV- RCV DCV= 128 cubic-feet Area (sq ft) Runoff Factor A x RF Weighted RF Impervious 2535 0.9 2282
Landscape 263 0.3 79
Pavers 0 0.1 0
Total 2798 2360 0.84
HMP Tree Well Multiplier per County BMPDM (D soil, 36" soil depth) 3.17 DCV x Tree Well Multiplier 405 cf
30-ft Diameter Mature Canopy Tree provides 420 cf

1205 Melrose Way
ATTACHMENT 2 - HYDROMODIFICATION MANAGEMENT CONTROLS:

SUPPORT DOCUMENTATION & CHECKLIST
❑ Check this box if this attachment is empty because the project is exempt from PDP hydromodification management requirements.

Each of the attachments indicated below should be considered for inclusion with the SWAMP. Use this checklist to indicate which attachments are included behind this coversheet.

Attachment Contents Checklist
Sequence
Attachment 2A Hydromodification
❑X Included
Management Exhibit
See Hydromodification Management Exhibit
Checklist on the back of this Attachment cover
sheet.

Attachment 2B Management of Critical Coarse 0 Exhibit showing project drainage boundaries Sediment Yield Areas marked on WMAA Critical Coarse Sediment Yield See Section 6.2 of the BMP Area Map
Design Manual. Analyses, as applicable,for Critical Coarse Sediment Yield Area Determination, per BMP Design Manual:
❑ 6.2.1 Verification of Geomorphic Landscape
Units Onsite
❑ 6.2.2 Downstream Systems Sensitivity to Coarse
Sediment
❑ 6.2.3 Optional Additional Analysis of Potential
Critical Coarse Sediment Yield Areas Onsite
Attachment 2C Geomorphic Assessment of 0 Not performed Receiving Channels
❑ Included
See Section 6.3.4 of the BMP ❑ Submitted as separate stand-alone document Design Manual.

Attachment 2D Flow Control Facility Design, 0 Included including Structural BMP
❑
Drawdown Calculations and Submitted as separate stand-alone document Overflow Design Summary
See Chapter 6 and Appendix G
of the BMP Design Manual
Attachment 2E Vector Control Plan ❑ Included
0 Not required because BMPs will drain in less
than 96 hours

Page 33 of 38 ends

BMP-1
Worksheet B.5-1: Simple Sizing Method for Biofiltration BMPs 1 lRemaining DCV After implementing retention BMPs 3404.0 cu-ft Partial Retention
2 Infiltration rate from Worksheet D.5-1 if partial infiltration is feasible 0.00 in/hr 3 Allowable drawdown time for aggregate storage below the underdrain 36 hours 4 Depth of runoff that can be infiltrated [Line 2 x Line 3] 0.00 inches 5 Aggregate pore space 0.95 in/in
6 1 Required depth of gravel below the underdrain [Line 4/ Line 51 0.00 inches 7 Assumed surface area of the biofiltration BMP 2300.0 sq-ft 8 Media retained pore storage 0.1 in/in 9 Volume retained pore storage 345.00 cu-ft 10 DCV that requires biofiltration [Line 1 - Line 91 3059.0 cu-ft BMP Parameters
11 Surface Ponding [6 inch minimum, 12 inch maximum] 12.0 inches 12 Media Thickness [18 in Min], also add mulch layer thicknes to this line 18 inches Aggregate Storage above underdrain invert(12 inches typical) - Use 0 inches for 13 38.4 inches
sizing if the aggregate is not over the entire bottom surface area 14 Freely drained pore storage 0.2 in/in Media filtration rate to be used for sizing (5 in/hr. with no outlet control; if the 15 filtration rate is controlled by the outlet, use the outlet controlled rate which will 2.634 in/hr be less than 5 in/hr.)
Baseline Calculations
16 Allowable Routing Time for sizing 6 hours 17 Depth filtered during storm [Line 15 x Line 161 16 inches Depth of Detention Storage

52.08 inches
18 [Line 11+ (Line 12 x Line 14) + (Line 13 x Line 5)] 19 ITotal Depth Treated [Line 17 + Line 18] 1 67.88 1 inches Option 1 - Biofilter 1.5 times the DCV
20 Required biofiltered volume [1.5 x Line 10] 4589 cu-ft 21 Required Footprint [Line 20/ Line 191 x 12 811.1 sq-ft Option 2 - Store 0.75 of remaining DCV in pores and poding 22 Required Storage (surface+ pores) Volume [0.75 x Line 10] 2294 cu-ft 23 Required Footprint [Line 22/Line 18] x 12 529 sq-ft Footprint of the BMP
24 Area draining to the BMP 105794 sq-ft Adjusted Runoff Factor for drainage area

0.59 25 (Refer to Appendix 13.1 and 13.2)
26 BMP Footprint Sizing Factor(Default 0.03 or an alternative minimum footprint 0.03 sizing factor from Worksheet 13.5-2, Line 11)
EMinimum BMP Footprint [Line 24 x Line 25 x Line 26] 1873 sq-ft 27 28 Footprint of the BMP= Maximum (Minimum(Line 21, Line 23), Line 27) 1873 sq-ft

Appendix B: Storm Water Pollutant Control Hydrologic Calculations and Sizing Methods °� os
o�
08 p9/ g S in
o
�g �9
C , f
p8
� o
c!-auwc t .s r.

San Diego County ,k
85 th Percentile Isopluvials
QB
Legend
1351h PEeCENTfLE ISOPLUVIAL r G? _ f
L.._ INCORPORATED CITY
h 6
O ?
NOTE' b
The 55th percentile u a 24 111
It represetns a value such spar 85%of the
oCsil 24 hour ramrall totals,will be less - thanthatvalue
Y N
3 N m )
0,55
_ O
0 r,4l,R A vls _.
i y
I
E� yE1a'.uur�Po��MnFBI �WrtM p,�a "'t f' LU E�
•xr.n inx u.s Y
�emr�^n4M+nii x•.n xw'o?.ArAxll9M•+� m _- f IF k',•- = GIs,
o.a�wurva;,w�� s.cw rne�.s. z - n ^.
�-
r.aw.ra�inmwars�r A+�•r..w xraw-n, +�l 6� ��t.l..•.s..t..- r-.eneuro�tirc:�mwxn.z�a
Figure B.1-1: 85th Percentile 24-hour Isopluvial Map
www.sandiegocounty.gov/stormwater B-6 Effective January 1, 2019

1205 Melrose Way
ATTACHMENT 2A - HYDROMODIFICATION MANAGEMENT EXHIBIT
For Attachment 2A, provide map(s)for the project site, titled "Hydromodification Management Exhibit." The checklist below identifies minimum elements that must be included with the exhibit. ❑ Underlying hydrologic soil group
❑ Approximate depth to groundwater
❑ Existing natural hydrologic features (watercourses, seeps, springs,wetlands, etc.) ❑ Critical coarse sediment yield areas to be protected
❑ Existing topography and impervious areas
❑ Existing and proposed site drainage network and storm drain structures ❑ Proposed connections to offsite drainage
❑ Proposed demolition
❑ Proposed grading
❑ Proposed impervious features
❑ Proposed design features and surface treatments used to minimize imperviousness ❑ Points of Compliance for hydromodification management ❑ Existing and proposed drainage boundary and drainage area to each Point of Compliance (when necessary, create separate exhibits for pre-development and post-project conditions) ❑ Structural BMPs for hydromodification management (location, type, and size)

Page 34 of 38 ends

TG PER PLAN FREEBOARD
DEN
BRUg1 SEE TABLE HEREON I
L 3 PVC SCREW CAP 6 WSE � / 3636 BROOKS BOX i T I3657 `` ` t l / _ � _� - - ,, / / I III = -_ - ABOVE GRADE CONIC
I / " �` - �- f - « -III-III-III- - CARER PANSA PLANTING, 3705 � (� 364.E �-- � �S CONC 4 x / «IOLA� I II 1111 DENSE ��_ - III _ OR APPROVED OTHER, 6 WEIR c� ----------------------- o / I I /� TREES / _ I III - - -t=3 9 -� '�_ - I -III-III- ?1 PER LANDSCAPE PLANS Q z 5o O CON
.y D NSE / s _
I . 7 / � �3666 /3�6 /3636 ;I "� ) 1 B USH„ 1 � ` ` 2:1 (SELF-MITIGATING 4 w =� �- � o z I r EXISTING ACC�C S VE -�, �� - - - "I� I =III=I - FIG PER PLAN 2.5' INLET 12"WEIR p w w /\//\�/ / / / I II1,755 SF _ ' WEIR NOTCH PONDING LU _ /\/\\%\\%
I - - - - - - - - - - - -„--�,--r, ,->� - - _ '/ � 1 I \` \\ III I- ��J EXTEND AND WRAP LINER 12" MIN. -III=III_ -- �/\//\////\\/ I I �94// 1361 III -III-I I 1=1 I 1=1 I 1=III-III-III III-III-III III-III-III -I Imo\ \\ ENGINEERED FILL LAYER SHALL BE I I / I 1 \- �\ III I r PAST EDGE OFBERM -III-III-III-III-III-III-I °° -III-III-III-III-III-I =� / MINIMUM 18" DEEP"SANDY LOAM" SOIL 370.5 x / I 365.6 / / 3626
I � �O6 \, I ► I " ,-I III-I�I-III-III-III-III III-III-I I III-III-III I I-I I I I I \ / / I I x / I \ II III I = MIX WITH NO MORE THAN 5% CLAY I 1 3665 ( 3636 I \ 36,5 I I TDENSE REES I - III-III-III-III-III-I I-III-III- -III-III-I - , CONTENT. PERCOLATION RATE I I 37L6 / I I x x I I, Q N BACKFILL IN BASIN,AND TO 5' OUTSIDE -I I I I -I I I-I I I-III-III-III III-III-III III-III-III I- \\/\\ I I 3696� / I O 1 °°NC , �34N4C _ 5-101N/HR MINIMUM.

I I / I - III I: Q I( II JIJI- I 347. SHALL CONSIST OF A 2-SACK MIX OF =1 1=1 1=1 1=1 =I =I�=I I I=I =I I =I I =I \ / I , s > l / I3656 I W \ I","I III s > 348f L LI L _ /\ n I I I ,: / I 3625 I , \_ J_35R5 _ w Il r r a a v`r _ IIJII JI4Z9 0 34.6 SLURRY -III=I \\/ 3 NON PERFORATED rIL I I / STANDPIPE 364.E I I D 3676 13 _ o �I I ~~ L - - ~I 'I - ____ ---- BOTTOM AND SIDES OF FLOW THROUGH PLANTER SHALL BE -I I \\\ a I ~ CONC , ' ' ' ' `M1 3464 -348- a- FLU 3665 / I Q I- - \ f Ilal ENSE ~ - ~"I r I x 35 34 ASPH - - _ LINED WITH 30 MIL PVC MEMBRANE THAT IS COVERED BY A _I I - - PERMAVOID LAYER ASPH MINIMUM OF 12 INCHES OF CLEAN SOIL, FREE FROM ROCKS I- Ix5 "' r 1 I I \\` ` ` ` -` 6J - AND DEBRIS,WITH A MAXIUM 3:1WITH A MAXIMUM 3:1 -III=III= QJG / /� \/\/\ WATER TIGHT CAP ON ,� � �- x '�\\ a,as .�x.B -#`��o= - - - - - - -=COND=== -III-I I / / / / \i\\/\\/\\/\ \\/\\/\\/\\/\� . �J- HORIZONTAL:VERTICAL[H:V]) SLOPE INCLINATION, ORTERMINAL END OF PIPE � , ` , SELF-MITIGATING (
aR� \ , \ DENSE - ^ FLATTER,AND MEETS THE FOLLOWING MINIMUM / FLOW CONTROL ORIFICE 6" DIAMETER PERFORATION PVC I I / 1 \ _TREES _ _ - 3 9 SF 3624 I \ I s \� _ _____ - ___ i_ SPECIFICATIONS: o PLATE PER DETAIL SUBDRAIN SHALL BE ENCAPSULATED IN - l - - -- - - ��- - -1- - - 9'G GRAVEL. GRAVEL AND SUBDRAIN SHALL °"°°g°"- SPECIFIC GRAVITY(ASTM D792): 1.2(G/CC, MIN.);TENSILE -�
- - - -- - BASIN WITH - �+�-��- OUTFACE PIPE BE WRAPPED IN MIRAFI 140N OR EQUAL. ��4 -1, � � (ASTM D882): 73 (LB/IN WIDTH, MIN); ELONGATION AT BREAK CONNECTION TO CATCH \ ' 361`. LOT A \ \ " 3sR \ (ASTM D882 380 %, MIN MODULUS ASTM D882 30 MIRAFI 140N OR EQUAL 2 DENSE � \ )� ( ), ( )• DRILLED ORFICE PLATE / / \ r \ (LB/IN-WIDTH, MIN.);AND TEAR STRENGTH (ASTM D1004): 8 (NON-WOVEN GEOTEXTILE) TREES "NOTE:(LB/IN, MIN); SEAM SHEAR STRENGTH (ASTM D882)58.4(LB/IN, **NOTE: BACKFILL FOR STORM DRAIN PIPES ENTERING OR EXISTING \ FIG 357.6 MIN); SEAM PEEL STRENGTH (ASTM D882) 15 (LB/IN, MIN). BASIN SHOULD BE BACKFILLED WITH A 2-SACK MIX OF SLURRY DENSE
BRUSH ,�.� r r = ` ` ` ` \ 360 �,300 SF � \ a PROVIDE 18-INCH OVERLAPPED,TAPED OR MIN 6 3 \\ `` = r = ° ` ` GLUED SEAMS AT ALL SEAMS. PLACE 3„ l ORFICE PLATE MIN. SQUARE DIMENSIONS 1.0 FT \ I \ 352.5 NON-WOVEN FILTER FABRIC(MIRAFI 140N OR 1 GREATER THAN PIPE DIA. HOT-DIP GALVANIZED 3 \" 3535 \ASPH x EQUAL) ON EITHER SIDE OF PVC LINER TO PROTECT LINER PLATE AFTER HOLES HAVE BEEN DRILLED FROM PUNCTURE ON ALL SIDES, "SANDWHICHING"THE PVC INFLOW PIPE } LINER WITH A FABRIC CUSHION.
364.7 \ \ I'' \ 36 I I \ \ SELF-MITIGATING ~ \� 359.E I \ \ x5 « SIZE OF DRILLED ORFICE PER 2,054 SIF ~ I \ t 45 BIOFILTRATION BASIN TABLE o s / , � _ 112" MAX DENSE I I 3636 I \ ~" \ DMA 1- ° " TABLE HEREON / BRUSH I I � = BASIN NO. ENGINEERED PERMAVOID TOTAL FREE ORIFICE / s r r r t a \ t t BRUSH3555 „ 3653 5 « = SOIL LAYER LAYER PONDING BOARD355 3l8" DIA. HOLE I1 TDENSEREES O4 \ ~ y �«� = 1 18" 38.4" 12" 1.0' 1.5" FLOW CONTROL ORFICE PLATE 367.6 c
\ 3645 _
- BIOFILTRATION BASIN DETAIL
BRUSH DENSE " 3�=
TREES 35F 5 3573�
365.E I / « "
3677 N.T.S.

L
362.7 \
\ \ 364.5 Ir \ -� , DMA DATA TABLE I \ BRUSH \ � \ - DMA NO. IMPERVIOUS PERVIOUS TOTAL \ 3666 ) 3656 - / \ \ O \ ` - AREA(S.F.) AREA(S.F.) AREA(S.F.) / DENSE ~
359.J r-
t 368.7 \ \ l ,", ~ \ 36x` I I , , s , 369.3 'Q \ 367�.6 I 1 TREES y I \ 3684 \ \ s s , , , , , ` � ~ w 1-1 53,174 52,620 105,794 LU
\ \�\ - 365- \ N 360.5 2-1 5,171 537 5,708 ASPH
�16. 4 (~/) - - SELF-
.. . . . . 361.5
I t r r r \ ----- -----� r-� U I - �� MITIGATING 4,188SF BMP NOTES II \^ -
3695 l / 36� \ \\ I I Z \ ROCKS M` ` ` Q 0 I DE-MINIMUS 275 SF 1. THESE BMPS AREA MANDATORY TO BE INSTALLED PER MANUFACTURER'S _ _.3 CONC 3696 \ 3676 I ^^ I 364.4 \\ -36¢- 3636 BRUSH M / L AREA RECOMMENDATIONS OR THERE PLANS I I 3695 x II \ x \ 366.4 \ � '}_ .

LO ' I I INFEASIBLE 2. NO CHANGES TO THE PROPOSED BMPS ON THIS SHEET WITHOUT PRIOR APPROVAL 6%.4 ` _ ` C'�'D 9 , 9 'r~ I TO ----- ----- 2,346 SF FORM THE CITY ENGINEERING DEPARTMENT 6 1 , r I I TREAT 3. NO SUBSTITUTIONS TO THE MATERIAL TYPES OR PLANTING TYPES WITHOUT PRIOR BRUSH APPROVAL FROM THE LAND DEVELOPMENT ENGINEER 3646 36 I I I 4. NO OCCUPANCY WILL BE GRANTED UNTIL THE CITY INSPECTOR STAFF HAS I I p J \\ \ 3676 """ \\ \� INSPECTED THIS PROJECT FOR APPRORIATE BMP CONSTRUCTION AND I370.E I « p IT ' = '�' x � �, 5 36s546 I I GENERAL INFORMATION INSTALLATION. 3694 \"� \ , ' ' ' ' \ ', , ' • ',, , , , _ ° ' 1 I I I PROJECT SITE IS LOCATED IN THE LOS MONOS H.S.A. (904.31)OF I 3704 \ _ \ « O ~ I I 3646 AGUA HEDIONDA CREEK H.A. OF CARLSBAD H.U., HOWEVER WATER QUALITY TECHNICAL REPOT I \ , " 3656 - - Z - J I DRAINAGE FROM THE SITE ULTIMATELY DISCHARGES TO THE I I 37�'4 \\ 3704 •` " \- � 368.5 , '^ x = I o © 3647 RECIEVING WATERS OF BUENA VISTA CREEK H.S.A. (904.22)OF TITLE PRIORITY DEVELOPMENT PROJECT STORM WATER QUALITY I « Y I{1\ BUENA VISTA CREEK H.A. OF CARLSBAD H.U. 3687 H � � Y \ a r r a t x , , � \- - - - _ � w --- - - - - I MANAGEMENT REPORT FOR 1205 MELROSE WAY B I DATE-MARCH 2021
- :5 064 I POLUTTANTS OF CONCERN-BENTHIC COMMUNITY EFFECTS, 4 O� q I I -I PREPARED BY-PASCO LARET SUITER&ASSOCIATES

BIFENTHRIN, SELENIUM, TOXICITY, INDICATOR BACTERIA,
I3:/4 371.8 \ I ;- \ \}��� ' ' ' ' ' ' ' ' ' _ \ _ " I�i NUTRIENTS,AND SEDIMENTATION/SILTATION 3 z26 \ I x 377.5 \ t` r JT..6 s \ J - �372.3 \ \ slat , x ` 37Q8 -- 5- I M 4` 49 101 MAINTENANCE AGREEMENT DOCUMENT 3732
- 3726 q t ~" , \\1 I37RB I DECK 36:3 � I LID SITE DESIGN BMP'S 3703
x 3705 \ - -�L � I \`" �365f -r I TITLE- \ DECK POOL 3 - 1 y\ �" x r II I 1. BIOFILTRATION BASIN DATE- 725I/ r ' ' I L L, I I v/ I I , , III PREPARED BY- I \ �x I/ J73.5 I l o l 13709 I I / -r 1 1 "" I (/ « II 3735 , J x I �J Ihhhh' I I I^^" / 37f.3 CONp 2. ROOF DRAIN TO LANDSCAPING x -DECK 3. MINIMIZE IMPERVIOUS SURFACES -a � -comic L ._ I I �- _ _ I�� � I _ _ � OPERATIONS AND MAINTENANCE PLAN �f 370.5 \
I \ 370.9 I
/ I I « t r�CON�
o - -� 37x5 1 �a~ , , , > , , , I I I \ r - 1 ,�h , , 4. PROTECT SLOPES AND CHANNELS Q " 3743 �'r \ 9--i -'-'' /�^ - I 369.3\«,- I .85 « r I r , > TITLE-STORM WATER OPERATIONS& MAINTENANCE PLAN FOR 1205 MELROSE WAY o I - r alsJt 374.E x o C-NC- I I I « ~ I j3649 DATE-MARCH 2O21 AS I x 5. TREE WELLS
x 374.s I ` - D 14 I I I V /I z 364B I PREPARED BY-PASCO LARET SUITER&ASSOCIATES 3755 � x
Cl) S6� d37.8 La � DENSER I^\EE �� � 2= .51 �st� SOURCE CONTROL BMP'S L - - ' � _ DES \ �� ` I 364B r � RESPONSIBLE PARTY INFORMATION x - \ 375..6 " �� , , , TREE WELL#1fV52 I ASP" ":' 376.5it` " f�, > �o =� ` ` /AREA 275 SF I� 1. STORM DRAIN STENCILING w _ I"-
6 3767 DE-MINIMIS 3642 . ZORAN DJORDJEVICH I J76.7
x 3764 ELROSE qY `�\ 3727 , 'r r ` a r a r ` a r ,` ` 2. EMPLOY INTEGRATED PEST MANAGEMENT PRACTICES d 378..5 376.8 �- x 375.7 x " ' - r a - 4 i _ _ ° ` _ 551 LYNWOOD DRIVE SIGN 0 • -� 374.4 / 3734 \ l /P`` 6 \ / 6 " 4 i CONC 375..7 \ - �� 37,.7 / / 2,346 SF / _ _ SOIL INFORMATION LEGEND
x 3646 J 3638
-
�� a ^ \ -2 3636 -�- w ', N ` - - - ��_ - �M- -_ 44 CNC _ DESCRIPTION SYMBOL o HYDROLOGIC SOIL GROUP:TYPE D LOT NUMBER 10
co
CIO
m
POST-CONSTRUCTION PERMANENT BMP OPERATION GROUND WATER INFORMATION DRAINAGE DIRECTION & MAINTENANCE PROCEDURE DETAILS
GROUND WATER WAS NOT ENCOUNTERED AT THE SITE. SEE DRAINAGE MANAGEMENT AREA g 0 40 80 120 REPORT PREPARED BY: GEOSOILS, INC Li STORM WATER MANAGEMENT AND DISCHARGE CONTROL MAINTENANCE DATED: MARCH 5, 2021 W.O. 8058-A-SC TYPE-B CURB INLET Z AGREEMENT APPROVAL NO: BROOKS BOX ❑ SCALE: 1" =40' 0&M RESPONSBILE PARTY DESIGNEE: PACIFIC INTERNATIONAL INVESTMENTS, INC N HORIZONTAL DATUM: NAD 83 COARSE SEDIMENT YIELD RIP RAP BMP ID# BMP TYPE SYMBOL QUANTITY DETAIL PLAN DETAIL CONSTRUCTION BMP DESCRIPTION INSPECTION MAINTENANCE MAINTENANCE METHOD QUANTITY SHEET SET SHEET NO. NO. NORTHING FASTING CONFIRMATION FREQUENCY FREQUENCY NUMBER(S) w 30 REFER TO SEDIMENT MENTYIELD A A THIS REPORT FOR CRITICAL PASCO CARET SUITER � O LAONDSDRAIN
INGO PAD)(TWO
PER EDUCATION PROGRAM (SOURCE CONTROL) ANNUAL AS NEEDED EMPLOYEE EDUCATION PROGRAM N/A N/A COARSE SEDIMENT YIELD AREAS WITHIN THIS PROJECT SITE. DMA EXHIBIT 0 a O BIOFILTRATION 1 SIGNAGE &STENCILING ANNUAL AS NEEDED REPAIR AND/OR REPLACE AS 3 N/A 1205 MELROSE WAY o ASSG ATES N AREA
NECESSARY VISTA, CA
STORM DRAIN MOWING AND DEBRIS COLLECTION San Diego I Solana Beach I Orange County CD O STENCILING • 3 BIOFILTRATION BASIN ANNUAL AS NEEDED AS NECESSARY. REPAIR AS NEEDED 1 N/A SCALE: 1'=40' Phone 858.259.82121 www. isaen ineerin com CD DATE:AUGUST 2021 P g g• 0 Fo
TREE WELL 2 TREE WELL MONTHLY AS NEEDED INSPECT TREE HEALTH& 2 N/A SHEET 1 OF 1

REPAIR/REPLACE AS NECCESSARY

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ATTACHMENT 2d

3334 Melrose
9/1/2021

SWMM MODEL SCHEMATICS
PRE-PROJECT MODEL POST-PROJECT MODEL
-
Oceanside
1 I
1 1
BmP-1
1 ;
S
4 DIV BYPASS STOR
l y
1 �
1 �
1p�/� �
r{.c-111
* y` OUTLETSTRUCTURE

UNDERDRAIN
`4 PO�y-,IC/,
-1
J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\Output\3334_SWMM_Schematics.xlsx

3334 Melrose
9/1/2021
POC-1

PRE-PROJECT
Width Weighted Weighted Weighted
(Area/Flow % D Infiltration Suction Initial DMA N-pery Area (ac) Length) (ft) %Slope % Impervious % C Soils Soils (in/hr): Head (in): Deficit:

DMA-1 0.06 2.53 163 3.0% 0% 0% 100% 0.025 9.000 0.330 Total: 2.53

POST-PROJECT
Width Weighted Weighted Weighted
(Area/Flow % D Infiltration Suction Initial DMA N-pery Area (ac) Length) (ft) %Slope % Impervious % C Soils Soils (in/hr): Head (in): Deficit:

DMA-1 0.06 2.377 1954 1.0% 51% 0% 100% 0.019 9.000 0.330 BMP-1 0.06 0.0528 58 0.0% 0.0% 0% 100% 0.025 9.000 0.330 SM 0.06 0.096 418 50.0% 0.0% 0% 100% 0.019 9.000 0.330 Total: 2.53
Infiltration: Suction Head: Initial Deficit:

D 0.025 in/hr D 9 in D 0.33
J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\3334 SWMM Input Alt4.xlsx

POC-1
[TITLE]
;;Project Title/Notes
3334 Melrose
Pre-Project Condition
[OPTIONS]
;;Option Value
FLOW UNITS CFS
INFILTRATION GREEN AMPT
FLOW ROUTING KINWAVE
LINK OFFSETS DEPTH
MIN SLOPE 0
ALLOW PONDING NO

SKIP STEADY STATE NO
START DATE 08/28/1951
START TIME 05:00:00
REPORT START DATE 08/28/1951
REPORT START TIME 05:00:00
END DATE 05/23/2008
END TIME 23:00:00
SWEEP START 01/01
SWEEP END 12/31
DRY DAYS 0
REPORT STEP 01:00:00
WET STEP 00:15:00
DRY STEP 04:00:00
ROUTING STEP 0:01:00
RULE STEP 00:00:00

INERTIAL DAMPING PARTIAL

NORMAL FLOW LIMITED BOTH

FORCE MAIN EQUATION H-W
VARIABLE STEP 0.75
LENGTHENING_STEP 0
MIN SURFAREA 12.557
MAX TRIALS 8
HEAD TOLERANCE 0.005
SYS FLOW TOL 5
LAT FLOW TOL 5
MINIMUM STEP 0.5
THREADS 1
[EVAPORATION]
;;Data Source Parameters
. .-------------- ----------------
MONTHLY .06 .08 .11 .15 .17 .19 .19 .18 .15 .11 .08 .06 DRY ONLY NO
[RAINGAGES]
;;Name Format Interval SCF Source

POC-1
-------------- --------- ------ ------ ----------
Oceanside INTENSITY 1:00 1.0 TIMESERIES Oceanside [SUBCATCHMENTS]
;;Name Rain Gage Outlet Area %Impery Width %Slope CurbLen SnowPack . .-------------- ---------------- ---------------- -------- -------- -------- -------- -------- ---------------- DMA-1 Oceanside poc-1 2.53 0 163 3 0
[SUBAREAS]
;;Subcatchment N-Impery N-Pery S-Impery S-Pery PctZero RouteTo PctRouted . .-------------- ---------- ---------- ---------- ---------- ---------- ---------- ---------- DMA-1 0.012 0.06 0.05 0.1 25 OUTLET
[INFILTRATION]
;;Subcatchment Suction Ksat IMD
. .-------------- ---------- ---------- ----------
DMA-1 9 0.025 0.33
[OUTFALLS]
;;Name Elevation Type Stage Data Gated Route To . .-------------- ---------- ---------- ---------------- -------- ---------------- ;Basin 1
POC-1 0 FREE NO
[TIMESERIES]
;;Name Date Time Value
Oceanside FILE "J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWQMP\SWMM\Rain Data\oceanside.dat" [REPORT]
;;Reporting Options

SUBCATCHMENTS ALL

NODES ALL

LINKS ALL
[TAGS]
[MAP]
DIMENSIONS 0.000 0.000 10000.000 10000.000
Units None
[COORDINATES]
;;Node X-Coord Y-Coord
POC-1 687.023 2569.975
[VERTICES]
;;Link X-Coord Y-Coord
[Polygons]

POC-1
;;Subcatchment X-Coord Y-Coord
. .-------------- ------------------ ------------------ DMA-1 636.132 5750.636
[SYMBOLS]
;;Gage X-Coord Y-Coord
. .-------------- ------------------ ------------------ Oceanside 1000.000 7500.000

POC-1
[TITLE]
;;Project Title/Notes
3334 Melrose
Post-Project Condition
[OPTIONS]
;;Option Value
FLOW UNITS CFS
INFILTRATION GREEN AMPT
FLOW ROUTING KINWAVE
LINK OFFSETS DEPTH
MIN SLOPE 0
ALLOW PONDING NO

SKIP STEADY STATE NO
START DATE 08/28/1951
START TIME 05:00:00
REPORT START DATE 08/28/1951
REPORT START TIME 05:00:00
END DATE 05/23/2008
END TIME 23:00:00
SWEEP START 01/01
SWEEP END 12/31
DRY DAYS 0
REPORT STEP 01:00:00
WET STEP 00:15:00
DRY STEP 04:00:00
ROUTING STEP 0:01:00
RULE STEP 00:00:00

INERTIAL DAMPING PARTIAL

NORMAL FLOW LIMITED BOTH

FORCE MAIN EQUATION H-W
VARIABLE STEP 0.75
LENGTHENING_STEP 0
MIN SURFAREA 12.557
MAX TRIALS 8
HEAD TOLERANCE 0.005
SYS FLOW TOL 5
LAT FLOW TOL 5
MINIMUM STEP 0.5
THREADS 1
[EVAPORATION]
;;Data Source Parameters
. .-------------- ----------------
MONTHLY .06 .08 .11 .15 .17 .19 .19 .18 .15 .11 .08 .06 DRY ONLY NO
[RAINGAGES]
;;Name Format Interval SCF Source

POC-1
-------------- --------- ------ ------ ----------
Oceanside INTENSITY 1:00 1.0 TIMESERIES Oceanside [SUBCATCHMENTS]
;;Name Rain Gage Outlet Area %Impery Width %Slope CurbLen SnowPack . .-------------- ---------------- ---------------- -------- -------- -------- -------- -------- ---------------- DMA-1 Oceanside BMP-1 2.377 51 1954 1 0 BMP-1 Oceanside DIV 0.0528 0 58 0 0
SM Oceanside POC-1 0.096 0 418 50 0
[SUBAREAS]
;;Subcatchment N-Impery N-Pery S-Impery S-Pery PctZero RouteTo PctRouted . .-------------- ---------- ---------- ---------- ---------- ---------- ---------- ---------- DMA-1 0.012 0.06 0.05 0.1 25 OUTLET
BMP-1 0.012 0.06 0.05 0.1 25 OUTLET
SM 0.012 0.06 0.05 0.1 25 OUTLET
[INFILTRATION]
;;Subcatchment Suction Ksat IMD
. .-------------- ---------- ---------- ----------
DMA-1 9 0.019 0.33
BMP-1 9 0.025 0.33
SM 9 0.019 0.33
[LID CONTROLS]
;;Name Type/Layer Parameters
BMP-1 BC
BMP-1 SURFACE 12 0 0 0 5
BMP-1 SOIL 18 0.4 0.2 0.1 5 5 1.5 BMP-1 STORAGE 38.4 0.99 0 0
BMP-1 DRAIN 0.3017 0.5 0 6 0 0 [LID USAGE]
;;Subcatchment LID Process Number Area Width InitSat FromImp ToPery RptFile DrainTo FromPery
. .-------------- ---------------- ------- ---------- ---------- ---------- ---------- ---------- ------------------------ ------------ ---- ----------
BMP-- BMP-1 1 2299.97 0 0 100 0
0 [OUTFALLS]
;;Name Elevation Type Stage Data Gated Route To ;Basin 1
POC-1 0 FREE NO
[DIVIDERS]
;;Name Elevation Diverted Link Type Parameters . .-------------- ---------- ---------------- ---------- ---------- DIV 0 BYPASS CUTOFF 0.131 0 0 0 0

MCA
[STORAGE]
;;Name Elev. MaxDepth InitDepth Shape Curve Name/Params N/A Fevap Psi Ksat IMD . .-------------- -------- ---------- ----------- ---------- ---------------------------- -------- -------- -------- -------- STOR 0 1.5 0 TABULAR STOR 0 0 [CONDUITS]
;;Name From Node To Node Length Roughness InOffset OutOffset InitFlow MaxFlow . .-------------- ---------------- ---------------- ---------- ---------- ---------- ---------- ---------- ---------- BYPASS DIV STOR 400 0.01 0 0 0 0 UNDERDRAIN DIV POC-1 100 0.013 0 0 0 0 [OUTLETS]
;;Name From Node To Node Offset Type QTable/Qcoeff Qexpon Gated OUTLETSTRUCTURE STOR POC-1 0 TABULAR/DEPTH OUTLET NO [XSECTIONS]
;;Link Shape Geoml Geom2 Geom3 Geom4 Barrels Culvert . .-------------- ------------ ---------------- ---------- ---------- ---------- ---------- ---------- BYPASS DUMMY 0 0 0 0 1 UNDERDRAIN DUMMY 0 0 0 0 1 [CURVES]
;;Name Type X-Value Y-Value
. .-------------- ---------- ---------- ----------
OUTLET Rating 0 0
OUTLET 0.05 0.04
OUTLET 0.1 0.1
OUTLET 0.15 0.19
OUTLET 0.2 0.29
OUTLET 0.25 0.4
OUTLET 0.3 0.53
OUTLET 0.35 0.66
OUTLET 0.4 0.81
OUTLET 0.45 0.97
OUTLET 0.5 1.13
OUTLET 0.55 1.71
OUTLET 0.6 2.63
OUTLET 0.65 3.78
OUTLET 0.7 5.1
OUTLET 0.75 6.59
OUTLET 0.8 8.22
OUTLET 0.85 9.98
OUTLET 0.9 11.68
OUTLET 0.95 11.72
OUTLET 1 11.77
OUTLET 1.05 11.82
OUTLET 1.1 11.86
OUTLET 1.15 11.91
OUTLET 1.2 11.96

POC-1
OUTLET 1.25 12.01
OUTLET 1.3 12.05
OUTLET 1.35 12.1
OUTLET 1.4 12.14
OUTLET 1.45 12.19
OUTLET 1.5 12.24
STOR Storage 0 2713
STOR 1.5 3380
[TIMESERIES]
;;Name Date Time Value
. .-------------- ---------- ---------- ----------
Oceanside FILE "J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWQMP\SWMM\Rain Data\oceanside.dat" [REPORT]
;;Reporting Options

SUBCATCHMENTS ALL

NODES ALL

LINKS ALL
[TAGS]
[MAP]
DIMENSIONS 0.000 0.000 10000.000 10000.000
Units None
[COORDINATES]
;;Node X-Coord Y-Coord
. .-------------- ------------------ ------------------ POC-1 687.023 2569.975
DIV 668.246 4037.017
STOR 2445.227 4048.055
[VERTICES]
;;Link X-Coord Y-Coord
. .-------------- ------------------ ------------------ [Polygons]
;;Subcatchment X-Coord Y-Coord
. .-------------- ------------------ ------------------ DMA-1 646.172 5869.184
BMP-1 668.246 5019.324
SM -886.598 4402.062
[SYMBOLS]
;;Gage X-Coord Y-Coord
Oceanside 1000.000 7500.000

SWMM OUTPUT REPORT PRE-PROJECT CONDITION
EPA STORM WATER MANAGEMENT MODEL - VERSION 5.1 (Build 5.1.013) -------------------------------------------------------------- 3334 Melrose
Pre-Project Condition
********************************************************* NOTE: The summary statistics displayed in this report are based on results found at every computational time step, not just on results from each reporting time step.
********************************************************* ****************
Analysis Options
****************
Flow Units . . . . . . . . . . . .... CFS
Process Models:

Rainfall/Runoff . . . . . . . . YES
RDII . . . . . . . . . . . . . . . . . . . NO
Snowmelt . . . . . . . . . . . . . . . NO
Groundwater . . . . . . . . . . . . NO
Flow Routing . . . . . . . . . . . NO
Water Quality . . . . . . .... NO
Infiltration Method . . . . . . GREEN_AMPT
Starting Date . . . . . . . . . . . . 08/28/1951 05:00:00 Ending Date . . . . . . . . . . . . . . 05/23/2008 23:00:00 Antecedent Dry Days . . . . . . 0.0
Report Time Step . . . . . . . . . 01:00:00
Wet Time Step . . . . . . . . . . . . 00:15:00
Dry Time Step . . . . . . . . . . . . 04:00:00
************************** Volume Depth
Runoff Quantity Continuity acre-feet inches
************************** --------- -------
Total Precipitation . . . . . . 142.331 675.090
Evaporation Loss . . . . . . . . . 5.220 24.757 Infiltration Loss . . . . . . . . 111.843 530.483
Surface Runoff . . . . . . . . . . . 27.735 131.549 Final Storage . . . . . . . . . . . . 0.000 0.001 Continuity Error (o) . . . . . -1.733
************************** Volume Volume
Flow Routing Continuity acre-feet 10^6 gal
**************************
Dry Weather Inflow . . . . . . . 0.000 0.000
Wet Weather Inflow . . . . . . . 27.735 9.038
Groundwater Inflow .. . . . . . 0.000 0.000
J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\Output\3334_PreProject_SWMM_resu Its POC-1.docx

SWMM OUTPUT REPORT PRE-PROJECT CONDITION
RDII Inflow . . . . . . . . . . . . . . 0.000 0.000 External Inflow .. . . . . . . . . 0.000 0.000 External Outflow . . . . . . . . . 27.735 9.038
Flooding Loss . . . . . . . . . . . . 0.000 0.000 Evaporation Loss . . . . . . . . . 0.000 0.000 Exfiltration Loss ........ 0.000 0.000
Initial Stored Volume .... 0.000 0.000
Final Stored Volume . . . . . . 0.000 0.000
Continuity Error (%) . . . . . 0.000
***************************
Subcatchment Runoff Summary
***************************
------------------------------------------------------------------------------------------------------------------------------ Total Total Total Total Impery Pery Total Total Peak Runoff Precip Runon Evap Infil Runoff Runoff Runoff Runoff Runoff Coeff Subcatchment in in in in in in in 10^6 gal CFS ------------------------------------------------------------------------------------------------------------------------------ DMA-1 675.09 0.00 24.76 530.48 0.00 131.55 131.55 9.04 2.77 0.195 Analysis begun on: Wed Sep 1 13:06:55 2021
Analysis ended on: Wed Sep 1 13:07:32 2021
Total elapsed time: 00:00:37
J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\Output\3334_PreProject_SWMM_resu Its POC-1.docx

SWMM OUTPUT REPORT POST-PROJECT CONDITION
EPA STORM WATER MANAGEMENT MODEL - VERSION 5.1 (Build 5.1.013) -------------------------------------------------------------- 3334 Melrose
Post-Project Condition
WARNING 04: minimum elevation drop used for Conduit BYPASS WARNING 04: minimum elevation drop used for Conduit UNDERDRAIN ********************************************************* NOTE: The summary statistics displayed in this report are based on results found at every computational time step, not just on results from each reporting time step.
********************************************************* ****************
Analysis Options
****************
Flow Units . . . . . . . . . . . . . . . CPS
Process Models:

Rainfall/Runoff . . . . . . . . YES
RDII . . . . . . . . . . . . . . . . . . . NO
Snowmelt . . . . . . . . . . . . . . . NO
Groundwater . . . . . . . . . . . . NO
Flow Routing . . . . . . . . . . . YES
Ponding Allowed . . . . . . . . NO
Water Quality . . . . . . . . . . NO
Infiltration Method . . . . . . GREEN AMPT
Flow Routing Method . . . . . . KINWAVE
Starting Date . . . . . . . . . . . . 08/28/1951 05:00:00 Ending Date . . . . . . . . . . . . . . 05/23/2008 23:00:00 Antecedent Dry Days . . . . . . 0.0
Report Time Step . . . . . . . . . 01:00:00
Wet Time Step . . . . . . . . . . . . 00:15:00
Dry Time Step . . . . . . . . . . . . 04:00:00
Routing Time Step . . . . . . . . 60.00 sec
************************** Volume Depth
Runoff Quantity Continuity acre-feet inches
************************** --------- -------
Initial LID Storage . . . . . . 0.008 0.038
Total Precipitation . . . . . . 142.095 675.090
Evaporation Loss . . . . . . . . . 16.340 77.631 Infiltration Loss .. . . . . . . 50.122 238.128
Surface Runoff . . . . . . . . . . . 9.079 43.135 LID Drainage . . . . . . . . . . . . . 68.585 325.848 Final Storage . . . . . . . . . . . . 0.016 0.075 Continuity Error (%) . . . . . -1.435
************************** Volume Volume
Flow Routing Continuity acre-feet 10^6 gal
*************************+ --------- --------- J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\Output\3334_PostProject_SWMM_resu Its POC-1.docx

SWMM OUTPUT REPORT POST-PROJECT CONDITION
Dry Weather Inflow . . . . . . . 0.000 0.000
Wet Weather Inflow . . . . . . . 77.665 25.308
Groundwater Inflow . . . . . . . 0.000 0.000
RDII Inflow . . . . . . . . . . . . . . 0.000 0.000 External Inflow . . . . . . . . . . 0.000 0.000 External Outflow . . . . . . . . . 77.655 25.305
Flooding Loss . . . . . . . . . . . . 0.000 0.000 Evaporation Loss . . . . . . . . . 0.000 0.000 Exfiltration Loss . . . . . . . . 0.000 0.000 Initial Stored Volume . . . . 0.000 0.000
Final Stored Volume . . . . . . 0.000 0.000
Continuity Error (%) . . . . . 0.012
********************************
Highest Flow Instability Indexes
++++++++++++++++++++++++++++++++
All links are stable.
+++++++++++++++++++++++++
Routing Time Step Summary
*************************
Minimum Time Step 60.00 sec
Average Time Step 60.00 sec
Maximum Time Step 60.00 sec
Percent in Steady State 0.00
Average Iterations per Step 1.00
Percent Not Converging 0.00
***************************
Subcatchment Runoff Summary
+++++++++++++++++++++++++++
------------------------------------------------------------------------------------------------------------------------------ Total Total Total Total Impery Pery Total Total Peak Runoff Precip Runon Evap Infil Runoff Runoff Runoff Runoff Runoff Coeff Subcatchment in in in in in in in 10^6 gal CFS ------------------------------------------------------------------------------------------------------------------------------ DMA-1 675.09 0.00 61.78 234.03 299.27 89.71 388.98 25.11 2.78 0.576 BMP-1 675.09 17511.15 892.35 0.00 0.00 0.00 17292.81 24.79 2.79 0.951 SM 675.09 0.00 21.99 470.68 0.00 197.04 197.04 0.51 0.11 0.292 ***********************
LID Performance Summary
-------------------------------------------------------------------------------------------------------------------- Total Evap Infil Surface Drain Initial Final Continuity Inflow Loss Loss Outflow Outflow Storage Storage Error Subcatchment LID Control in in in in in in in o -------------------------------------------------------------------------------------------------------------------- BMP-1 BMP-1 18186.24 892.38 0.00 1705.27 15588.17 1.80 2.66 -0.00 J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\Output\3334_PostProject_SWMM_resu Its POC-1.docx

SWMM OUTPUT REPORT POST-PROJECT CONDITION
******************
Node Depth Summary
++++++++++++++++++
--------------------------------------------------------------------------------- Average Maximum Maximum Time of Max Reported
Depth Depth HGL Occurrence Max Depth
Node Type Feet Feet Feet days hr:min Feet --------------------------------------------------------------------------------- POC-1 OUTFALL 0.00 0.00 0.00 0 00:00 0.00 DIV DIVIDER 0.00 0.00 0.00 0 00:00 0.00 STOR STORAGE 0.00 0.60 0.60 18857 12:16 0.60 +++++++++++++++++++
Node Inflow Summary
*******************
------------------------------------------------------------------------------------------------- Maximum Maximum Lateral Total Flow
Lateral Total Time of Max Inflow Inflow Balance Inflow Inflow Occurrence Volume Volume Error
Node Type CFS CFS days hr:min 10^6 gal 10^6 gal Percent ------------------------------------------------------------------------------------------------- POC-1 OUTFALL 0.11 2.86 18857 12:01 0.514 25.3 0.000 DIV DIVIDER 2.79 2.79 18857 12:16 24.8 24.8 0.000 STOR STORAGE 0.00 2.66 18857 12:16 0 2.25 0.134 *********************
Node Flooding Summary
*********************
No nodes were flooded.
++++++++++++++++++++++
Storage Volume Summary
**********************
-------------------------------------------------------------------------------------------------- Average Avg Evap Exfil Maximum Max Time of Max Maximum Volume Pcnt Pcnt Pcnt Volume Pcnt Occurrence Outflow Storage Unit 1000 ft3 Full Loss Loss 1000 ft3 Full days hr:min CFS -------------------------------------------------------------------------------------------------- STOR 0.001 0 0 0 1.712 37 18857 12:16 2.66 ***********************
Outfall Loading Summary
***********************
----------------------------------------------------------- Flow Avg Max Total
J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\Output\3334_PostProject_SWMM_resu Its POC-1.docx

SWMM OUTPUT REPORT POST-PROJECT CONDITION
Freq Flow Flow Volume
Outfall Node Pcnt CFS CFS 10^6 gal
----------------------------------------------------------- POC-1 4.08 0.05 2.86 25.303
----------------------------------------------------------- System 4.08 0.05 2.86 25.303
++++++++++++++++++++
Link Flow Summary
----------------------------------------------------------------------------- Maximum Time of Max Maximum Max/ Max/
IFlowl Occurrence IVelocl Full Full
Link Type CFS days hr:min ft/sec Flow Depth ----------------------------------------------------------------------------- BYPASS DUMMY 2.66 18857 12:16
UNDERDRAIN DUMMY 0.13 9626 09:48
OUTLETSTRUCTURE DUMMY 2.66 18857 12:16
*************************
Conduit Surcharge Summary
+++++++++++++++++++++++++
No conduits were surcharged.

Analysis begun on: Wed Sep 1 13:18:12 2021
Analysis ended on: Wed Sep 1 13:19:05 2021
Total elapsed time: 00:00:53
J:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\Output\3334_PostProject_SWMM_resu Its POC-1.docx

POC-1
Peak Flow Frequency Summary
Return Period Pre-project Qpeak Post-project- Mitigated Q (cfs) (cfs)
LF = 0.1xQ2 0.118 0.065
2-year 1.184 0.653
5-year 1.592 1.182
10-year 1.909 1.857
1:\ACTIVE JOBS\3334 MELROSE WAY\CIVIL\REPORTS\SWAMP\SWMM\3334 SWMM_PostProcessing Alt4.xlsx

POC-1
Peak Flow Frequency Curves

2.000

1.500 000
000
10 U
C
3 0
LLA —0—Pre-project Qpeak
�e 1.000
m
v
a
06 nil --&-POSt-project Mitigated Qpeak

0.500

0.000
0 1 2 3 4 5 6 7 8 9 10 Return Period in Years

Low-flow Threshold: 10% = POC-1

0.1xQ2 (Pre): 0.118 cfs
Q10(Pre): 1.909 cfs
Ordinate M 100
Incremental Q(Pre): 0.01791 cfs
Total Hourly Data: 497370 hours The proposed BMP:J PASSED Pre-project Flow Pre-project% Post-project Post-project Interval Pre-project Hours Percentage Pass/Fail (cfs) Time Exceeding Hours Time Exceeding
0 0.118 873 1.76E-03 942 1.89E-03 108% Pass 1 0.136 806 1.62E-03 416 8.36E-04 52% Pass 2 0.154 733 1.47E-03 295 5.93E-04 40% Pass 3 0.172 664 1.34E-03 252 5.07E-04 38% Pass 4 0.190 615 1.24E-03 220 4.42E-04 36% Pass 5 0.208 560 1.13E-03 198 3.98E-04 35% Pass 6 0.226 520 1.05E-03 173 3.48E-04 33% Pass 7 0.244 481 9.67E-04 158 3.18E-04 33% Pass 8 0.262 447 8.99E-04 142 2.86E-04 32% Pass 9 0.280 425 8.54E-04 127 2.55E-04 30% Pass 10 0.297 396 7.96E-04 120 2.41E-04 30% Pass 11 0.315 367 7.38E-04 108 2.17E-04 29% Pass 12 0.333 339 6.82E-04 99 1.99E-04 29% Pass 13 0.351 312 6.27E-04 92 1.85E-04 29% Pass 14 0.369 298 5.99E-04 90 1.81E-04 30% Pass 15 0.387 279 5.61E-04 86 1.73E-04 31% Pass 16 0.405 265 5.33E-04 81 1.63E-04 31% Pass 17 0.423 242 4.87E-04 78 1.57E-04 32% Pass 18 0.441 225 4.52E-04 75 1.51E-04 33% Pass 19 0.459 210 4.22E-04 71 1.43E-04 34% Pass 20 0.477 203 4.08E-04 66 1.33E-04 33% Pass 21 0.494 196 3.94E-04 62 1.25E-04 32% Pass 22 0.512 179 3.60E-04 56 1.13E-04 31% Pass 23 0.530 171 3.44E-04 54 1.09E-04 32% Pass 24 0.548 162 3.26E-04 51 1.03E-04 31% Pass 25 0.566 150 3.02E-04 48 9.65E-05 32% Pass 26 0.584 139 2.79E-04 45 9.05E-05 32% Pass 27 0.602 126 2.53E-04 44 8.85E-05 35% Pass 28 0.620 122 2.45E-04 42 8.44E-05 34% Pass 29 0.638 113 2.27E-04 41 8.24E-05 36% Pass 30 0.656 108 2.17E-04 38 7.64E-05 35% Pass 31 0.673 101 2.03E-04 36 7.24E-05 36% Pass 32 0.691 96 1.93E-04 32 6.43E-05 33% Pass 33 0.709 92 1.85E-04 31 6.23E-05 34% Pass 34 0.727 88 1.77E-04 31 6.23E-05 35% Pass 35 0.745 86 1.73E-04 29 5.83E-05 34% Pass 36 0.763 86 1.73E-04 29 5.83E-05 34% Pass 37 0.781 79 1.59E-04 29 5.83E-05 37% Pass 38 0.799 74 1.49E-04 28 5.63E-05 38% Pass 39 0.817 71 1.43E-04 28 5.63E-05 39% Pass 40 0.835 67 1.35E-04 27 5.43E-05 40% Pass 41 0.853 63 1.27E-04 26 5.23E-05 41% Pass 42 0.870 60 1.21E-04 25 5.03E-05 42% Pass 43 0.888 59 1.19E-04 23 4.62E-05 39% Pass 44 0.906 57 1.15E-04 22 4.42E-05 39% Pass 45 0.924 54 1.09E-04 22 4.42E-05 41% Pass 46 0.942 53 1.07E-04 18 3.62E-05 34% Pass 47 0.960 50 1.01E-04 16 3.22E-05 32% Pass 48 0.978 47 9.45E-05 15 3.02E-05 32% Pass 49 0.996 45 9.05E-05 14 2.81E-05 31% Pass 50 1.014 43 8.65E-05 14 2.81E-05 33% Pass 51 1.032 42 8.44E-05 14 2.81E-05 33% Pass 52 1.049 40 8.04E-05 14 2.81E-05 35% Pass 53 1.067 38 7.64E-05 14 2.81E-05 37% Pass 54 1.085 38 7.64E-05 14 2.81E-05 37% Pass

Pre-project Flow Pre-project% Post-project Post-project Interval Pre-project Hours Percentage Pass/Fail (cfs) Time Exceeding Hours Time Exceeding
55 1.103 38 7.64E-05 14 2.81E-05 37% Pass 56 1.121 35 7.04E-05 14 2.81E-05 40% Pass 57 1.139 35 7.04E-05 14 2.81E-05 40% Pass 58 1.157 33 6.63E-05 14 2.81E-05 42% Pass 59 1.175 33 6.63E-05 14 2.81E-05 42% Pass 60 1.193 32 6.43E-05 12 2.41E-05 38% Pass 61 1.211 31 6.23E-05 12 2.41E-05 39% Pass 62 1.229 30 6.03E-05 12 2.41E-05 40% Pass 63 1.246 29 5.83E-05 12 2.41E-05 41% Pass 64 1.264 28 5.63E-05 12 2.41E-05 43% Pass 65 1.282 27 5.43E-05 12 2.41E-05 44% Pass 66 1.300 26 5.23E-05 12 2.41E-05 46% Pass 67 1.318 26 5.23E-05 11 2.21E-05 42% Pass 68 1.336 22 4.42E-05 10 2.01E-05 45% Pass 69 1.354 22 4.42E-05 9 1.81E-05 41% Pass 70 1.372 21 4.22E-05 9 1.81E-05 43% Pass 71 1.390 20 4.02E-05 9 1.81E-05 45% Pass 72 1.408 20 4.02E-05 9 1.81E-05 45% Pass 73 1.425 20 4.02E-05 9 1.81E-05 45% Pass 74 1.443 20 4.02E-05 9 1.81E-05 45% Pass 75 1.461 19 3.82E-05 9 1.81E-05 47% Pass 76 1.479 18 3.62E-05 9 1.81E-05 50% Pass 77 1.497 17 3.42E-05 9 1.81E-05 53% Pass 78 1.515 16 3.22E-05 8 1.61E-05 50% Pass 79 1.533 16 3.22E-05 8 1.61E-05 50% Pass 80 1.551 15 3.02E-05 8 1.61E-05 53% Pass 81 1.569 14 2.81E-05 8 1.61E-05 57% Pass 82 1.587 13 2.61E-05 8 1.61E-05 62% Pass 83 1.605 12 2.41E-05 8 1.61E-05 67% Pass 84 1.622 11 2.21E-05 8 1.61E-05 73% Pass 85 1.640 11 2.21E-05 8 1.61E-05 73% Pass 86 1.658 10 2.01E-05 8 1.61E-05 80% Pass 87 1.676 9 1.81E-05 8 1.61E-05 89% Pass 88 1.694 9 1.81E-05 8 1.61E-05 89% Pass 89 1.712 9 1.81E-05 8 1.61E-05 89% Pass 90 1.730 9 1.81E-05 8 1.61E-05 89% Pass 91 1.748 9 1.81E-05 7 1.41E-05 78% Pass 92 1.766 8 1.61E-05 6 1.21E-05 75% Pass 93 1.784 7 1.41E-05 5 1.01E-05 71% Pass 94 1.801 6 1.21E-05 5 1.01E-05 83% Pass 95 1.819 6 1.21E-05 5 1.01E-05 83% Pass 96 1.837 5 1.01E-05 5 1.01E-05 100% Pass 97 1.855 5 1.01E-05 5 1.01E-05 100% Pass 98 1.873 5 1.01E-05 5 1.01E-05 100% Pass 99 1.891 5 1.01E-05 5 1.01E-05 100% Pass 100 1.909 5 1.01E-05 5 1.01E-05 100% Pass

POC-1
Flow Duration Curve
[Pre vs. Post (Mitigated)]

2.500

2.000 1 1 1 1 1 1 1 1 1 1 _4

1.500
3 3 Pre-project Q
6 Post-project(Mitigated)Q

1.000
ta

0.500

0.000

1.0E-06 1.0E-05 1.0E-04 1.0E-03 1.0E-02 Time Exceeding

POC-1
SWMM Model Flow Coefficient Calculation and
Effective Ponding Depth Calculation
BMP-1
Bio-Retention Cell
PARAMETER ABBREV. LID BMP
Ponding Depth PD 12 in
Bioretention Soil Layer S 18 in
Permavoid Layer G 38.4 in
TOTAL 5.7 ft
68 in
Orifice Coefficient cg 0.6 --
Low Flow Orifice Diameter D 1.45 in
Drain exponent n 0.5 --
Flow Rate (volumetric) Q 0.131 cfs
Ponding Depth Surface Area APp 2300 ft2
Bioretention Surface Area AS,AG 2300 ftz
AS,AG 0.0528 a
Porosity of Bioretention Soil n 0.40 -
Flow Rate (per unit area) q 6.157 in/hr
Effective Ponding Depth PDeff 12.00 in
Flow Coefficient C 0.3017 1--

3334
Prepared by Pasco Laret Suiter & Associates Printed 9/1/2021 HydroCADO 10.10-6a s/n 10097 ©2020 HydroCAD Software Solutions LLC Page 17 Summary for Pond 25P: BMP-1 STOR
Volume Invert Avail.Storage Storage Description #1 101.00, 4,562 cf Biofiltration Basin (Conic) Listed below (Recalc) Elevation Surf.Area Voids Inc.Store Cum.Store Wet.Area (feet) (sq-ft) (%) (cubic-feet) (cubic-feet) (sq-ft) 101.00 2,713 0.0 0 0 2,713
101.50 2,929 100.0 1,410 1,410 2,949
102.00 3,151 100.0 1,520 2,930 3,191
102.50 3,380 100.0 1,632 4,562 3,442
Device Routing Invert Outlet Devices
#1 Primary 95.30' 12.00" Round Outlet
L= 10.0' RCP, groove end projecting, Ke= 0.200
Inlet/ Outlet Invert= 95.30'/95.20' S= 0.0100 '/' Cc= 0.900 n= 0.013, Flow Area= 0.79 sf
#2 Device 1 101.00' 6.00"W x 6.00" H Vert. Orifice X 2.00 C= 0.600 Limited to weir flow at low heads
#3 Device 1 101.50' 36.00"x 36.00" Horiz. Grate C= 0.600 in 36.00" x 36.00" Grate (100% open area)
Limited to weir flow at low heads

3334
Prepared by Pasco Laret Suiter & Associates Printed 9/1/2021 HydroCAD® 10.10-6a s/n 10097 ©2020 HydroCAD Software Solutions LLC Page 18 Stage-Discharge for Pond 25P: BMP-1 STOR
Elevation Primary
(feet) (cfs)
101.00 0.00
101.05 0.04
101.10 0.10
101.15 0.19
101.20 0.29
101.25 0.40
101.30 0.53
101.35 0.66
101.40 0.81
101.45 0.97
101.50 1.13
101.55 1.71
101.60 2.63
101.65 3.78
101.70 5.10
101.75 6.59
101.80 8.22
101.85 9.98
101.90 11.68
101.95 11.72
102.00 11.77
102.05 11.82
102.10 11.86
102.15 11.91
102.20 11 96
102.25 12.01
102.30 12.05
102.35 12.10
102.40 12.14
102.45 12.19
102.50 12.24

Drawdown Calculation for BMP-1
Project Name Melrose
Project No 3334
Surface Drawdown Time: 4.9 hr
Surface Area 2300 sq ft
Underdrain Orifice Diameter:
in

1.45 in
C: 0.6
Surface Ponding (to invert of lowest
surface discharge opening in outlet 1 ft
structure):

Amended Soil Depth: 1.5 ft
Permavoid Depth: 3.2 ft
Orifice Q = 0.131 cfs
Effective Depth 52.08 in
Infiltration controlled by soil 5.000 in/hr
Infiltration controlled by orifice 1 2.462 in/hr

TORY R. WALKER ENGINEERING

RELIABLE SOLUTIONS IN WATER RESOURCES
Manning's n Values for Overland Flow'
The BMP Design Manuals within the County of San Diego allow for a land surface description other than short prairie grass to be used for hydromodification BMP design only if documentation provided is consistent with Table A.6 of the SWMM 5 User's Manual.

In January 2016, the EPA released the SWMM Reference Manual Volume I — Hydrology (SWMM Hydrology Reference Manual). The SWMM Hydrology Reference Manual complements the SWMM 5 User's Manual by providing an in-depth description of the program's hydrologic components. Table 3-5 of the SWMM Hydrology Reference Manual expounds upon Table A.6 of the SWMM 5 User's Manual by providing Manning's n values for additional overland flow surfaces. Therefore, in order to provide SWMM users with a wider range of land surfaces suitable for local application and to provide Copermittees with confidence in the design parameters, we recommend using the values published by Yen and Chow in Table 3-5 of the EPA SWMM Reference Manual Volume I — Hydrology. The values are provided in the table below:

Overland Surface Manning value(n)
Smooth asphalt pavement 0.010
Smooth impervious surface 0.011
Tar and sand pavement 0.012
Concrete pavement 0.014
Rough impervious surface 0.015
Smooth bare packed soil 0.017
Moderate bare packed soil 0.025
Rough bare packed soil 0.032
Gravel soil 0.025
Mowed poor grass 0.030
Average grass, closely clipped sod 0.040
Pasture 0.040
Timberland 0.060
Dense grass 0.060
Shrubs and bushes 0.080
Land Use
Business 0.014
Semibusiness 0.022
Industrial 0.020
Dense residential 0.025
Suburban residential 0.030
Parks and lawns 0.040
1Content summarized from Improving Accuracy in Continuous Simulation Modeling: Guidance for Selecting Pervious Overland Flow Manning's n Values in the San Diego Region (TRWE, 2016).

WATERSHED,FLOODPLAIN&STORM WATER MANAGEMENT•RIVER RESTORATION•FLOOD FACILITIES DESIGN•SEDIMENT a EROSION 122 CIVIC CENTER DRIVE, SUITE 206, VISTA CA 92084 • 760-414-9212 • TRWENGINEERING.COM

Hydrologic Soil Group—San Diego County Area,California 3 (1205 Melrose Way)
475940 47-IOM 476000 476030 476060 476090 476120 33'11'11"N I 33°11'11"N
Bs
raft
� s �
a
it ot'be�vali��l t i
IS
33°11'3"N � i. 5 330 11'3"N
475940 475970 476000 476030 47M 476090 476120 3 3
Map Scale:1:1,220 if printed on A portrait(8.5"x 11")sheet Meters N
0 15 30 60 9D
Feet
0 50 100 200 300
Map projection:Web Mentor Comer coordinates:WG584 Edge tics:UTM Zone 11N WGS84 U}DA Natural Resources Web Soil Survey 12/28/2020 Conservation Service National Cooperative Soil Survey Page 1 of 4

Hydrologic Soil Group—San Diego County Area,California
(1205 Melrose Way)
MAP LEGEND MAP INFORMATION
Area of Interest(AOI) p C The soil surveys that comprise your AOI were mapped at Area of Interest(AOI) 0 C/D 1:24,000.

Soils D Warning:Soil Map may not be valid at this scale.

Soil Rating Polygons �
A p Not rated or not available Enlargement of maps beyond the scale of mapping can cause misunderstanding of the detail of mapping and accuracy of soil 0 A/D Water Features line placement.The maps do not show the small areas of Streams and Canals contrasting soils that could have been shown at a more detailed 0 B scale.

Transportation
0 B/D
Rails Please rely on the bar scale on each map sheet for map 0 C measurements.
'.,,r Interstate Highways
0 C/D US Routes Source of Map: Natural Resources Conservation Service Web Soil Survey URL:
0 D Major Roads Coordinate System: Web Mercator(EPSG:3857) Not rated or not available Local Roads
Maps from the Web Soil Survey are based on the Web Mercator Soil Rating Lines Background projection,which preserves direction and shape but distorts q distance and area.A projection that preserves area,such as the ® Aerial Photography Albers equal-area conic projection,should be used if more • A/D accurate calculations of distance or area are required. +'* B This product is generated from the USDA-NRCS certified data as B/D of the version date(s)listed below.
x C Soil Survey Area: San Diego County Area,California Survey Area Data: Version 15, May 27,2020
P1 0 C/D
Soil map units are labeled(as space allows)for map scales * r D 1:50,000 or larger.
r Not rated or not available Date(s)aerial images were photographed: Jan 24,2020—Feb Soil Rating Points 12,2020
p A The orthophoto or other base map on which the soil lines were compiled and digitized probably differs from the background p A/D imagery displayed on these maps.As a result,some minor B shifting of map unit boundaries may be evident.

B/D
UU� Natural Resources Web Soil Survey 12/28/2020 � Conservation Service National Cooperative Soil Survey Page 2 of 4

Hydrologic Soil Group—San Diego County Area,California 1205 Melrose Way Hydrologic Soil Group
Map unit symbol Map unit name Rating Acres in AOI Percent of AOI BsD Bosanko clay,9 to 15 D 0.2 6.9% percent slopes
PeC2 Placentia sandy loam,5 D 2.5 93.1% to 9 percent slopes,
eroded
Totals for Area of Interest 2.6 100.0%
Description
Hydrologic soil groups are based on estimates of runoff potential. Soils are assigned to one of four groups according to the rate of water infiltration when the soils are not protected by vegetation, are thoroughly wet, and receive precipitation from long-duration storms.

The soils in the United States are assigned to four groups (A, B, C, and D)and three dual classes (A/D, B/D, and C/D). The groups are defined as follows:

Group A. Soils having a high infiltration rate (low runoff potential)when thoroughly wet. These consist mainly of deep, well drained to excessively drained sands or gravelly sands. These soils have a high rate of water transmission.

Group B. Soils having a moderate infiltration rate when thoroughly wet. These consist chiefly of moderately deep or deep, moderately well drained or well drained soils that have moderately fine texture to moderately coarse texture.

These soils have a moderate rate of water transmission.

Group C. Soils having a slow infiltration rate when thoroughly wet. These consist chiefly of soils having a layer that impedes the downward movement of water or soils of moderately fine texture or fine texture. These soils have a slow rate of water transmission.

Group D. Soils having a very slow infiltration rate (high runoff potential)when thoroughly wet. These consist chiefly of clays that have a high shrink-swell potential, soils that have a high water table, soils that have a claypan or clay layer at or near the surface, and soils that are shallow over nearly impervious material. These soils have a very slow rate of water transmission.

If a soil is assigned to a dual hydrologic group (A/D, B/D, or C/D), the first letter is for drained areas and the second is for undrained areas. Only the soils that in their natural condition are in group D are assigned to dual classes. usDA Natural Resources Web Soil Survey 12/28/2020 Conservation Service National Cooperative Soil Survey Page 3 of 4

Appendix G: Guidance for Continuous Simulation and Hydromodification Management Sizing Factors
� t$0.IJ 9E RNARaINO — r—f
t t

RWERSIUE
; , 9 17 18
t R I V E R S I ❑
FiANG� :...... �I
u
33J .S A N D I E G D 1 M P E R I A 18 FL[FNIW
16 r
SHY UICGO � _
Figure G.1-2: California Irrigation Management Information System "Reference Evapotranspiration Zones"
G-5 February 2016

Appendix G: Guidance for Continuous Simulation and Hydromodification Management Sizing Factors Table G.1-1: Monthly Average Reference Evapotranspiration by ETo Zone (inches/month and inches/day) for use in SWMM Models for Hydromodification Management Studies in San Diego County CIMIS Zones 1, 4, 6, 9, and 16 (See CIMIS ETo Zone Map) January February March April May June July August September October November December Zone in/month in/month in/month in/month in/month in/month in/month in/month in/month in/month in/month in/month 1 0.93 1.4 2.48 3.3 4.03 4.5 4.65 4.03 3.3 2.48 1.2 0.62 4 1.86 2.24 3.41 4.5 5.27 5.7 5.89 5.58 4.5 3.41 2.4 1.86 6 1.86 2.24 3.41 4.8 5.58 6.3 6.51 6.2 4.8 3.72 2.4 1.86 9 2.17 2.8 4.03 5.1 5.89 6.6 7.44 6.82 5.7 4.03 2.7 1.86 16 1 1.55 1 2.52 1 4.03 1 5.7 1 7.75 1 8.7 1 9.3 18.37 1 6.3 1 4.34 1 2.4 1 1.55 January February Match April May June July August September October NovemberDecember Days 31 28 31 30 31 30 31 31 30 31 30 31 Zone in/day in/day in/day in/day in/day in/day in/day in/day in/day in/day in/day in/day 1 0.030 0.050 0.080 0.110 0.130 0.150 0.150 0.130 0.110 0.080 0.040 0.020 4 0.060 0.080 0.110 0.150 0.170 0.190 0.190 0.180 0.150 0.110 0.080 0.060 6 0.060 0.080 0.110 0.160 0.180 0.210 0.210 0.200 0.160 0.120 0.080 0.060 9 0.070 0.100 0.130 0.170 0.190 0.220 0.240 0.220 0.190 0.130 0.090 0.060 16 0.050 0.090 0.130 0.190 0.250 0.290 0.300 0.270 0.210 0.140 0.080 0.050 G-6 February 2016

1205 Melrose Way
ATTACHMENT 3 - BMP MAINTENANCE INFORMATION
Each of the attachments indicated below should be considered for inclusion with the SWAMP. Use this checklist to indicate which attachments are included behind this coversheet.

Attachment Contents Checklist
Sequence
Attachment 3A Structural BMP Operations ❑ Included and Maintenance Plan
See Structural BMP Maintenance Information
Checklist on the back of this Attachment cover sheet.

Attachment 3B Draft Maintenance ❑ Included
Agreement ❑ Not Applicable

Page 35 of 38 ends

1205 Melrose Way
ATTACHMENT 3A - MAINTENANCE PLAN REQUIREMENTS
For Attachment 3A, provide a BMP operation and maintenance plan (O&M Plan).The checklist below identifies minimum elements to be included with the O&M Plan. An O&M Plan template is available at:
http://www.cityofvista.com/services/city-departments/community-development/building-planning- permits-applications/land-development-autocad-templates/storm-water-forms ❑ Specific maintenance indicators and actions for proposed structural BMP(s).This shall be based on Section 7.7 of the BMP Design Manual and enhanced to reflect actual proposed components of the structural BMP(s)
❑ Use of O&M Plan template, or plan of equivalent content

Page 36 of 38 ends

Storm Water Operations & Maintenance Plan
for
1205 Melrose Way
1205 Melrose Way
Vista, CA
APN 166-184-10-00, 166-183-17-00, 184-184-09
PREPARED FOR:

Zoran Djordjevich
Encinitas, CA 92024
Prepared: March 2021
Revised: June 2021
W. Justin �uiter, RCE 68964 DATE
1 1205 Melrose Way
March 2021

TABLE OF CONTENTS

1.0 Operation and Maintenance Plan - Responsible Party 3

2.0 Project Site Summary 4

2.1 Vicinity Map 4

2.2 Project Description 5

2.3 Storm Water Mitigation Site Plan 5

2.4 Existing and Proposed Drainage Pattern and Storm Drain System 5

2.5 Identify Receiving Waters, Watershed and Hydrologic Unit Basin Number 5

2.6 Project Type and Activities 6

3.0 Summary of Storm Water Quality Management Plan (SWAMP) 6

4.0 Employee Training Program 7

5.0 Inspection Program 7

6.0 Maintenance Program 8

7.0 Record Keeping 8

8.0 Cost Estimate 8

9.0 Engineer of Work Statement 8
Appendix A - Storm Water Mitigation Site Map
Appendix B - Source Control BMPs
Appendix C- Structural Control BMPs
Appendix D - Employee Training Program
Appendix E - Inspection Program
Appendix F - Maintenance Program
Appendix G - Cost Estimate
2 1205 Melrose Way
March 2021

1.0 OPERATION AND MAINTENANCE PLAN — RESPONSIBLE PARTY This Operation and Maintenance (O&M) Plan addresses the requirements for the implementation of long-term operation and maintenance associated with the proposed permanent storm water BMPs constructed for 1205 Melrose Way approved by the City of Vista. For specific discussion on the selection of BMPs refer to the City of Vista approved Storm Water Quality Management Plan (SWAMP) for the project.

The responsible party for the long-term Operation and Maintenance of the onsite BMPs is the future HOA.
3 1205 Melrose Way
March 2021

2.0 Project Site Summary
The subject property is located at 1205 Melrose Way in the City of Vista. The site is on the west side of Melrose Drive and approximately 1 mile South of the CA-78 freeway. The site is approximately 2.57-acres. In the existing condition, the northwesterly portion of the site sheet flows southwest to northeast to a concrete ditch on the adjacent property that runs along the property line. The remaining portion of the site generally slopes south to the northeasterly corner to a concrete ditch on the adjacent property that ultimately drains to a storm drain main that runs north towards Breeze Hill Road.

The site is APN 166-184-10-00, 166-183-17-00, 166-184-09-00

2.1 Vicinity Map:

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4 1205 Melrose Way
March 2021

2.2 Project Description:

The project is classified as a "Priority Development Project". Therefore, it is subject to local storm water quality and hydromodification management requirements.

The project consists of a single-family residential subdivision. The subdivision will include 15 residential lots, open space lot, private street and driveway, and drainage improvements including a biofiltration basin BMP designed to provide pollutant control and hydromodification management flow control for the project's onsite storm water runoff to satisfy the local requirements. It is the intent of the developer that at subdivision buildout, the storm water biofiltration basin will be constructed on the open space lot and will be maintained by the future HOA.

Offsite improvements along Melrose Way that includes remove and replacement of the half-width of asphalt, construction of curb &gutter and sidewalk along the property frontage. There are two proposed tree wells to provide pollutant control treatment, hydromodification management, and volume retention requirements that will be maintained by the future HOA.

The project area consists of hydrologic soil group D. The project will not have slopes steeper than 2:1. All slopes will include slope protection for construction and post- construction.

2.3 Storm Water Mitigation Site Plan
Refer to Appendix A for the Storm Water Mitigation Site Plan.

2.4 Existing and Proposed Drainage Pattern and Storm Drain System In the existing condition, the northwesterly portion of the site sheet flows southwest to northeast to a concrete ditch on the adjacent property that runs along the property line. The remaining portion of the site generally slopes south to the northeasterly corner to a concrete ditch on the adjacent property that ultimately drains to a storm drain main that runs north towards Breeze Hill Road.

The grading plan has been prepared to show the extents of pad grading, and house and driveway coverage that will be constructed on each pad. In the proposed condition, onsite storm water runoff will be collected in proposed storm drain and conveyed to the proposed biofiltration basin.

The biofiltration basin provide hydromodification flow control that will outlet to the concrete ditch on the adjacent property.

The BMP totals an area of 2,300 square feet. This treatment area will provide hydromodification management flow control and storm water pollutant control for the project's onsite runoff. The proposed BMP area will be a community asset, maintained by the future subdivision HOA. Two tree wells along the property frontage along Melrose way will provide pollutant control treatment, 5 1205 Melrose Way
March 2021

hydromodification management, and volume retention requirements that will be maintained by the future HOA. Refer to the project's Storm Water Quality Management Plan (SWAMP) for the hydromodification management and pollutant control analysis.

2.5 Identify Receiving Waters, Watershed and Hydrologic Unit Basin Number The proposed project is located within the Carlsbad Hydrologic Unit (HU), Agua Hedionda Hydrologic Area (HA)- Los Monos Hydrologic Subarea (HSA),904.31 and Buena Vista 904.22.The surface, coastal, and groundwater receiving waters located in the area and downstream of this project include Agua Hedionda Creek and Lagoon. The designated beneficial uses of these waters include MUN, AGR, IND, REC1, REC2, BIOL, WARM, WILD, COMM, EST, RARE, MAR, AQUA, MIGR, SPWN, SHELL.

The Carlsbad HU is approximately 210 square miles in area extending from the headwaters above Lake Wolhford to the Pacific Ocean. In addition to the cities of Carlsbad, San Marcos and Encinitas, it includes substantial portions of Vista, Oceanside, Escondido, Solana Beach and the community of Rancho Santa Fe. The Carlsbad HU includes four major coastal lagoons, three lakes, and two large water storage reservoirs.The HU contains six hydrologic areas including Loma Alta (904.10), Buena Vista Creek (901.20), Agua Hedionda (904.30), Encinas (904.40), San Marcos (904.50), and Escondido Creek (904.60).

Based on Final 2012 Clean Water Act Section 303(d) Integrated Report (USEPA Final Approval July 30, 2015) Agua Hedionda Creek is listed as a 303(d) impaired water body. The pollutants listed are:

Enterococcus, Fecal Coliform, Manganese, Phosphorus, Selenium, Total Dissolved Solids, Total Nitrogen as N, and Toxicity.

Refer to:
http://www.waterboards.ca.gov/water_issues/programs/tmdl/integrated2012.shtml

2.6 Project Type and Activities
The project consists of a detached single-family subdivision with 15 residential lots. The anticipated activities are consistent with normal residential use. The anticipated pollutants to be generated by the land use are:

Detached Residential Development and Streets:
• Sediment
• Nutrients
• Trash and Debris
• Oxygen demanding substances
• Oil and Grease
• Bacteria and Viruses
6 1205 Melrose Way
March 2021

• Pesticides
• Heavy Metals
• Organic Compounds including petroleum hydrocarbons

3.0 Summary of Storm Water Quality Management Plan (SWAMP) The project is classified as a "Priority Development Project". Therefore, it is subject to local storm water quality and hydromodification management requirements.

To comply with storm water requirements, the project includes site design, source control and a treatment control BMP.The plans for the project detail the construction of a biofiltration basin which serves as the primary treatment control BMP.The biofiltration basin is designed to provide pollutant control and hydromodification management flow control for the project's onsite storm water runoff to satisfy the local requirements. The locations, details and pollutant control and hydromodification calculations are included in the approved SWQMP for the project on file with the City of Vista.

A summary of the project's BMPs are as follows:

1. Site Design:

Optimize the site layout; Use pervious surfaces; Disperse runoff; and Design Integrated Management Practices (IMPs)

2. Source Control:

Maintain on-site storm drain inlets; Limit Landscape/Outdoor Pesticide Use; Provide Efficient Irrigation; Sweep Streets

3. Treatment Control:

Biofiltration Basin

4.0 Employee Training Program
The BMP maintenance is the responsibility of the future HOA. The future HOA will be responsible to train personnel in the practices of maintenance and record keeping of the permanent BMPs.

All applicable employees will be trained in a timely fashion, and at a minimum will be trained within one month of hiring. Training and refreshment courses will occur at least one time a year.

Training shall include but not be limited to training for the inspection of all source control and treatment control BMP's.

An example Training Log is located in Appendix D.

5.0 Inspection Program
7 1205 Melrose Way
March 2021

At a minimum, the BMP shall be inspected annually or following significant rain events. Inspections shall be conducted by trained staff. An inspection form shall be completed with each inspection.

Inspection logs shall be kept for a minimum of five years.

In addition, the BMP owner must verify annually that the O&M Plan is being implemented by submitting a self-certification statement to the City of Vista. The verification must include a record of inspection of the BMPs prior to the rainy season (October 1st of each year).

An example Inspection Log is located in Appendix E.

6.0 Maintenance Program
The cost and expense of maintaining the storm water permanent BMP shall be the responsibility of and paid for by the legally responsible party, owner or the heir, assigns and successors in interest of each such owner. The storm water BMP facility constructed by the owners, or their successors, include, but are not limited to biofiltration basins, drainage inlets, etc., all as shown on City approved SWAMP on file with the City of Vista.

A Maintenance Log will be filled out and kept for each maintenance service. The records will be kept for a minimum of five years. An example Maintenance Log is located in Appendix F.

7.0 Record Keeping
The legally responsible entity designated in this document will be the source for record keeping.

Examples of Training, Inspection and Maintenance Logs are contained in the Appendices.

These shall be kept for a minimum of five years.

8.0 Cost Estimate
See Appendix G for the Cost Estimate.

9.0 Engineer of Work Statement
This Operation and Maintenance Ian w s prepa by Pasco Laret Suiter & Associates under the supervision of W. Jus in Su ter, P. .

W. Justin Su er, RCE 68964 DATE
1205 Melrose Way
March 2021

Appendix A — Storm Water Mitigation Site Plan
9 1205 Melrose Way
March 2021

TG PER PLAN FREEBOARD
DEN
BRUg1 SEE TABLE HEREON I
L 3 PVC SCREW CAP 6 WSE � / 3636 BROOKS BOX i T I3657 `` ` t l / _ � _� - - ,, / / I III = -_ - ABOVE GRADE CONIC
I / " �` - �- f - « -III-III-III- - CARER PANSA PLANTING, 3705 � (� 364.E �-- � �S CONC 4 x / «IOLA� I II 1111 DENSE ��_ - III _ OR APPROVED OTHER, 6 WEIR c� ----------------------- o / I I /� TREES / _ I III - - -t=3 9 -� '�_ - I -III-III- ?1 PER LANDSCAPE PLANS Q z 5o O CON
.y D NSE / s _
I . 7 / � �3666 /3�6 /3636 ;I "� ) 1 B USH„ 1 � ` ` 2:1 (SELF-MITIGATING 4 w =� �- � o z I r EXISTING ACC�C S VE -�, �� - - - "I� I =III=I - FIG PER PLAN 2.5' INLET 12"WEIR p w w /\//\�/ / / / I II1,755 SF _ ' WEIR NOTCH PONDING LU _ /\/\\%\\%
I - - - - - - - - - - - -„--�,--r, ,->� - - _ '/ � 1 I \` \\ III I- ��J EXTEND AND WRAP LINER 12" MIN. -III=III_ -- �/\//\////\\/ I I �94// 1361 III -III-I I 1=1 I 1=1 I 1=III-III-III III-III-III III-III-III -I Imo\ \\ ENGINEERED FILL LAYER SHALL BE I I / I 1 \- �\ III I r PAST EDGE OFBERM -III-III-III-III-III-III-I °° -III-III-III-III-III-I =� / MINIMUM 18" DEEP"SANDY LOAM" SOIL 370.5 x / I 365.6 / / 3626
I � �O6 \, I ► I " ,-I III-I�I-III-III-III-III III-III-I I III-III-III I I-I I I I I \ / / I I x / I \ II III I = MIX WITH NO MORE THAN 5% CLAY I 1 3665 ( 3636 I \ 36,5 I I TDENSE REES I - III-III-III-III-III-I I-III-III- -III-III-I - , CONTENT. PERCOLATION RATE I I 37L6 / I I x x I I, Q N BACKFILL IN BASIN,AND TO 5' OUTSIDE -I I I I -I I I-I I I-III-III-III III-III-III III-III-III I- \\/\\ I I 3696� / I O 1 °°NC , �34N4C _ 5-101N/HR MINIMUM.

I I / I - III I: Q I( II JIJI- I 347. SHALL CONSIST OF A 2-SACK MIX OF =1 1=1 1=1 1=1 =I =I�=I I I=I =I I =I I =I \ / I , s > l / I3656 I W \ I","I III s > 348f L LI L _ /\ n I I I ,: / I 3625 I , \_ J_35R5 _ w Il r r a a v`r _ IIJII JI4Z9 0 34.6 SLURRY -III=I \\/ 3 NON PERFORATED rIL I I / STANDPIPE 364.E I I D 3676 13 _ o �I I ~~ L - - ~I 'I - ____ ---- BOTTOM AND SIDES OF FLOW THROUGH PLANTER SHALL BE -I I \\\ a I ~ CONC , ' ' ' ' `M1 3464 -348- a- FLU 3665 / I Q I- - \ f Ilal ENSE ~ - ~"I r I x 35 34 ASPH - - _ LINED WITH 30 MIL PVC MEMBRANE THAT IS COVERED BY A _I I - - PERMAVOID LAYER ASPH MINIMUM OF 12 INCHES OF CLEAN SOIL, FREE FROM ROCKS I- Ix5 "' r 1 I I \\` ` ` ` -` 6J - AND DEBRIS,WITH A MAXIUM 3:1WITH A MAXIMUM 3:1 -III=III= QJG / /� \/\/\ WATER TIGHT CAP ON ,� � �- x '�\\ a,as .�x.B -#`��o= - - - - - - -=COND=== -III-I I / / / / \i\\/\\/\\/\ \\/\\/\\/\\/\� . �J- HORIZONTAL:VERTICAL[H:V]) SLOPE INCLINATION, ORTERMINAL END OF PIPE � , ` , SELF-MITIGATING (
aR� \ , \ DENSE - ^ FLATTER,AND MEETS THE FOLLOWING MINIMUM / FLOW CONTROL ORIFICE 6" DIAMETER PERFORATION PVC I I / 1 \ _TREES _ _ - 3 9 SF 3624 I \ I s \� _ _____ - ___ i_ SPECIFICATIONS: o PLATE PER DETAIL SUBDRAIN SHALL BE ENCAPSULATED IN - l - - -- - - ��- - -1- - - 9'G GRAVEL. GRAVEL AND SUBDRAIN SHALL °"°°g°"- SPECIFIC GRAVITY(ASTM D792): 1.2(G/CC, MIN.);TENSILE -�
- - - -- - BASIN WITH - �+�-��- OUTFACE PIPE BE WRAPPED IN MIRAFI 140N OR EQUAL. ��4 -1, � � (ASTM D882): 73 (LB/IN WIDTH, MIN); ELONGATION AT BREAK CONNECTION TO CATCH \ ' 361`. LOT A \ \ " 3sR \ (ASTM D882 380 %, MIN MODULUS ASTM D882 30 MIRAFI 140N OR EQUAL 2 DENSE � \ )� ( ), ( )• DRILLED ORFICE PLATE / / \ r \ (LB/IN-WIDTH, MIN.);AND TEAR STRENGTH (ASTM D1004): 8 (NON-WOVEN GEOTEXTILE) TREES "NOTE:(LB/IN, MIN); SEAM SHEAR STRENGTH (ASTM D882)58.4(LB/IN, **NOTE: BACKFILL FOR STORM DRAIN PIPES ENTERING OR EXISTING \ FIG 357.6 MIN); SEAM PEEL STRENGTH (ASTM D882) 15 (LB/IN, MIN). BASIN SHOULD BE BACKFILLED WITH A 2-SACK MIX OF SLURRY DENSE
BRUSH ,�.� r r = ` ` ` ` \ 360 �,300 SF � \ a PROVIDE 18-INCH OVERLAPPED,TAPED OR MIN 6 3 \\ `` = r = ° ` ` GLUED SEAMS AT ALL SEAMS. PLACE 3„ l ORFICE PLATE MIN. SQUARE DIMENSIONS 1.0 FT \ I \ 352.5 NON-WOVEN FILTER FABRIC(MIRAFI 140N OR 1 GREATER THAN PIPE DIA. HOT-DIP GALVANIZED 3 \" 3535 \ASPH x EQUAL) ON EITHER SIDE OF PVC LINER TO PROTECT LINER PLATE AFTER HOLES HAVE BEEN DRILLED FROM PUNCTURE ON ALL SIDES, "SANDWHICHING"THE PVC INFLOW PIPE } LINER WITH A FABRIC CUSHION.
364.7 \ \ I'' \ 36 I I \ \ SELF-MITIGATING ~ \� 359.E I \ \ x5 « SIZE OF DRILLED ORFICE PER 2,054 SIF ~ I \ t 45 BIOFILTRATION BASIN TABLE o s / , � _ 112" MAX DENSE I I 3636 I \ ~" \ DMA 1- ° " TABLE HEREON / BRUSH I I � = BASIN NO. ENGINEERED PERMAVOID TOTAL FREE ORIFICE / s r r r t a \ t t BRUSH3555 „ 3653 5 « = SOIL LAYER LAYER PONDING BOARD355 3l8" DIA. HOLE I1 TDENSEREES O4 \ ~ y �«� = 1 18" 38.4" 12" 1.0' 1.5" FLOW CONTROL ORFICE PLATE 367.6 c
\ 3645 _
- BIOFILTRATION BASIN DETAIL
BRUSH DENSE " 3�=
TREES 35F 5 3573�
365.E I / « "
3677 N.T.S.

L
362.7 \
\ \ 364.5 Ir \ -� , DMA DATA TABLE I \ BRUSH \ � \ - DMA NO. IMPERVIOUS PERVIOUS TOTAL \ 3666 ) 3656 - / \ \ O \ ` - AREA(S.F.) AREA(S.F.) AREA(S.F.) / DENSE ~
359.J r-
t 368.7 \ \ l ,", ~ \ 36x` I I , , s , 369.3 'Q \ 367�.6 I 1 TREES y I \ 3684 \ \ s s , , , , , ` � ~ w 1-1 53,174 52,620 105,794 LU
\ \�\ - 365- \ N 360.5 2-1 5,171 537 5,708 ASPH
�16. 4 (~/) - - SELF-
.. . . . . 361.5
I t r r r \ ----- -----� r-� U I - �� MITIGATING 4,188SF BMP NOTES II \^ -
3695 l / 36� \ \\ I I Z \ ROCKS M` ` ` Q 0 I DE-MINIMUS 275 SF 1. THESE BMPS AREA MANDATORY TO BE INSTALLED PER MANUFACTURER'S _ _.3 CONC 3696 \ 3676 I ^^ I 364.4 \\ -36¢- 3636 BRUSH M / L AREA RECOMMENDATIONS OR THERE PLANS I I 3695 x II \ x \ 366.4 \ � '}_ .

LO ' I I INFEASIBLE 2. NO CHANGES TO THE PROPOSED BMPS ON THIS SHEET WITHOUT PRIOR APPROVAL 6%.4 ` _ ` C'�'D 9 , 9 'r~ I TO ----- ----- 2,346 SF FORM THE CITY ENGINEERING DEPARTMENT 6 1 , r I I TREAT 3. NO SUBSTITUTIONS TO THE MATERIAL TYPES OR PLANTING TYPES WITHOUT PRIOR BRUSH APPROVAL FROM THE LAND DEVELOPMENT ENGINEER 3646 36 I I I 4. NO OCCUPANCY WILL BE GRANTED UNTIL THE CITY INSPECTOR STAFF HAS I I p J \\ \ 3676 """ \\ \� INSPECTED THIS PROJECT FOR APPRORIATE BMP CONSTRUCTION AND I370.E I « p IT ' = '�' x � �, 5 36s546 I I GENERAL INFORMATION INSTALLATION. 3694 \"� \ , ' ' ' ' \ ', , ' • ',, , , , _ ° ' 1 I I I PROJECT SITE IS LOCATED IN THE LOS MONOS H.S.A. (904.31)OF I 3704 \ _ \ « O ~ I I 3646 AGUA HEDIONDA CREEK H.A. OF CARLSBAD H.U., HOWEVER WATER QUALITY TECHNICAL REPOT I \ , " 3656 - - Z - J I DRAINAGE FROM THE SITE ULTIMATELY DISCHARGES TO THE I I 37�'4 \\ 3704 •` " \- � 368.5 , '^ x = I o © 3647 RECIEVING WATERS OF BUENA VISTA CREEK H.S.A. (904.22)OF TITLE PRIORITY DEVELOPMENT PROJECT STORM WATER QUALITY I « Y I{1\ BUENA VISTA CREEK H.A. OF CARLSBAD H.U. 3687 H � � Y \ a r r a t x , , � \- - - - _ � w --- - - - - I MANAGEMENT REPORT FOR 1205 MELROSE WAY B I DATE-MARCH 2021
- :5 064 I POLUTTANTS OF CONCERN-BENTHIC COMMUNITY EFFECTS, 4 O� q I I -I PREPARED BY-PASCO LARET SUITER&ASSOCIATES

BIFENTHRIN, SELENIUM, TOXICITY, INDICATOR BACTERIA,
I3:/4 371.8 \ I ;- \ \}��� ' ' ' ' ' ' ' ' ' _ \ _ " I�i NUTRIENTS,AND SEDIMENTATION/SILTATION 3 z26 \ I x 377.5 \ t` r JT..6 s \ J - �372.3 \ \ slat , x ` 37Q8 -- 5- I M 4` 49 101 MAINTENANCE AGREEMENT DOCUMENT 3732
- 3726 q t ~" , \\1 I37RB I DECK 36:3 � I LID SITE DESIGN BMP'S 3703
x 3705 \ - -�L � I \`" �365f -r I TITLE- \ DECK POOL 3 - 1 y\ �" x r II I 1. BIOFILTRATION BASIN DATE- 725I/ r ' ' I L L, I I v/ I I , , III PREPARED BY- I \ �x I/ J73.5 I l o l 13709 I I / -r 1 1 "" I (/ « II 3735 , J x I �J Ihhhh' I I I^^" / 37f.3 CONp 2. ROOF DRAIN TO LANDSCAPING x -DECK 3. MINIMIZE IMPERVIOUS SURFACES -a � -comic L ._ I I �- _ _ I�� � I _ _ � OPERATIONS AND MAINTENANCE PLAN �f 370.5 \
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6 3767 DE-MINIMIS 3642 . ZORAN DJORDJEVICH I J76.7
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x 3646 J 3638
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co
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m
POST-CONSTRUCTION PERMANENT BMP OPERATION GROUND WATER INFORMATION DRAINAGE DIRECTION & MAINTENANCE PROCEDURE DETAILS
GROUND WATER WAS NOT ENCOUNTERED AT THE SITE. SEE DRAINAGE MANAGEMENT AREA g 0 40 80 120 REPORT PREPARED BY: GEOSOILS, INC Li STORM WATER MANAGEMENT AND DISCHARGE CONTROL MAINTENANCE DATED: MARCH 5, 2021 W.O. 8058-A-SC TYPE-B CURB INLET Z AGREEMENT APPROVAL NO: BROOKS BOX ❑ SCALE: 1" =40' 0&M RESPONSBILE PARTY DESIGNEE: PACIFIC INTERNATIONAL INVESTMENTS, INC N HORIZONTAL DATUM: NAD 83 COARSE SEDIMENT YIELD RIP RAP BMP ID# BMP TYPE SYMBOL QUANTITY DETAIL PLAN DETAIL CONSTRUCTION BMP DESCRIPTION INSPECTION MAINTENANCE MAINTENANCE METHOD QUANTITY SHEET SET SHEET NO. NO. NORTHING FASTING CONFIRMATION FREQUENCY FREQUENCY NUMBER(S) w 30 REFER TO SEDIMENT MENTYIELD A A THIS REPORT FOR CRITICAL PASCO CARET SUITER � O LAONDSDRAIN
INGO PAD)(TWO
PER EDUCATION PROGRAM (SOURCE CONTROL) ANNUAL AS NEEDED EMPLOYEE EDUCATION PROGRAM N/A N/A COARSE SEDIMENT YIELD AREAS WITHIN THIS PROJECT SITE. DMA EXHIBIT 0 a O BIOFILTRATION 1 SIGNAGE &STENCILING ANNUAL AS NEEDED REPAIR AND/OR REPLACE AS 3 N/A 1205 MELROSE WAY o ASSG ATES N AREA
NECESSARY VISTA, CA
STORM DRAIN MOWING AND DEBRIS COLLECTION San Diego I Solana Beach I Orange County CD O STENCILING • 3 BIOFILTRATION BASIN ANNUAL AS NEEDED AS NECESSARY. REPAIR AS NEEDED 1 N/A SCALE: 1'=40' Phone 858.259.82121 www. isaen ineerin com CD DATE:AUGUST 2021 P g g• 0 Fo
TREE WELL 2 TREE WELL MONTHLY AS NEEDED INSPECT TREE HEALTH& 2 N/A SHEET 1 OF 1

REPAIR/REPLACE AS NECCESSARY

Appendix B — Source Control BMPs
10 1205 Melrose Way
March 2021

Chapter
C O U NTY OF S A N D 1 EGO BMP DES I G N MAN UAL
Source Control and Site
Design Requirements for All
Development Projects
This chapter presents general, source control, and site design requirements to be met by all Standard projects and PDPs. This Manual should be the first guidance document consulted during the development planning process.A second important County reference related to site design and source control is the Low Impact Development (LID) Handbook. The LID Handbook provides a comprehensive list of LID planning and stormwater management techniques for developers,builders, contractors, planners, landscape architects, engineers, and government employees. It can be found on the County's website:
http://www.sandiegocounty.gov/content/sdc/dpw/watersheds/DevelopmentandConstruction.html Specific requirements and limitations for each site design and source control BMP are contained in applicable SWQMP forms, and in corresponding instructions and attachments. In some cases, separate Fact Sheets have also been developed for individual BMPs. The content of these and other materials specified by the County provides further, more detailed articulation of the requirements generally described in this Chapter.

4.1 General Requirements (GR) and Guidance
Per MS4 Permit Provision E.3.a.(1) and WPO Section 67.811(a)(3), BMPs must be designed, constructed and maintained subject to the following criteria:

4.1.1. Onsite BMPs must be located so as to remove pollutants from runoff prior to its discharge to any receiving waters, and as close to the source as possible.

BMP location affects its ability to retain, and/or treat, the pollutants from the contributing drainage area.BMPs must remove pollutants from runoff and should be placed as close to the pollutant source as possible.

How to comply:Projects must implement source control(Section 4.2) and site design BMPs (Section

4.3) that are applicable to their project and site conditions. www.sandiegocounty.gov/stormwater 4-1 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects

4.1.2.•Structural BMPs must not be constructed within the Waters of the U.S.

Construction, operation, and maintenance of a structural BMP in a water body can negatively impact the physical, chemical, and biological integrity, as well as the beneficial uses, of the water body.

However,offsite alternative compliance opportunities involving restoration of areas within Waters of the U.S. may be identified by the County.

How to comply: Projects must prepare project plans depicting the location of receiving waters and proposed BMPs within the project boundary. These plans must demonstrate that storm water BMPs are not located within Waters of the U.S.

4.1.3. Onsite BMPs must be designed and implemented with measures to avoid the creation ofnuisances orpollutions associated with vectors (e.g. mosquitos, rodents, or flies).

According to the California Department of Health, structural BMPs that retain standing water for over 96 hours are particularly concerning for facilitating mosquito breeding. Certain site design features that hold standing water may similarly produce mosquitoes.

How to comply: Projects must incorporate design, construction, and maintenance principles demonstrating that they will drain retained water within 96 hours and minimize standing water.Design calculations must be provided to demonstrate the potential for standing water ponding at surface level and accessible to mosquitos has been addressed.

4.1.4.• Use caution when placing Structural BMPs in FEMA or County Floodplains and Floodways.

Placement of Structural BMPs within FEMA or County Floodplains or Floodways should be consulted with a wetland biologist to avoid future creation of habitat,where the S-BMP could become jurisdictional or connected to a jurisdictional area. If that is the case, an outside agency (such as the Army Corps of Engineers, Regional Water Quality Control Board, or California Department of Fish &Wildlife) may impose future restrictions on maintenance of these S-BMPs, and activities may need to be coordinated with those agencies,including processing of permits.

How to comply: Use caution when placing BMPs within the floodway or floodplain. Consult with applicable agencies if necessary.

Characteristics of a Floodplafn
• Floodplain
Flood Fringe NOW F[h e
Froodway
Nmrnaf Channel ago
Source.NAP Cvji o k,FEMA
www.sandiegocounty.gov/stormwater 4-2 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects

4.L5.•BMPs thatprovide for flood control detention in addition to water quality requirements and relationship to County Hydraulic Design Manual.

BMPs that are serving flood control purposes in addition to pollutant control and/or hydromodification management may not operate appropriately to satisfy the requirements of the County Hydraulic Design Manual.

How to comply: Consult the County Hydraulic Design Manual in addition to the Conjunctive Use handout that is posted in the Development Resources web page under Calculators and Modeling Software.

4.2 Source Control (SC) BMP Requirements
Source control BMPs avoid and reduce pollutants in storm water runoff. Everyday activities, such as recycling,trash disposal,and irrigation generate potential storm water pollutants.Source control BMPs are defined as activities or features that reduce the potential for storm water runoff to come into contact with pollutants. Per MS4 Permit Provision E.3.a.(2) and WPO Section 67.811(a)(4)), all development projects must implement source control BMPs where applicable and feasible.

How to comply:Projects must implement all source control BMPs that are applicable to their project.

Applicability should be determined through a consideration of the development project's proposed features and the anticipated pollutant sources associated with them.Appendix C provides guidance for identifying source control BMPs applicable to a project. Table 2 "Baseline BMPs for Pollutant- Generating Sources"located in Standard and PDP SWQMPs must be used to document compliance with these requirements. Table 2 applies to all projects except for Small Residential Projects. Small Residential Projects are those requiring either: a Building Permit, Minor Residential Grading Permit, or site Plan Permit for a single family home;or a Tentative Parcel Map Permit for up to 4 single family homes and a remainder parcel.

4.2.1 Prevent illicit discharges into the MS4
Per WPO Section 67.804,illicit discharges (i.e., discharges to the MS4 that are not composed entirely of storm water) are prohibited,except as exempted per WPO Section 67.805.Projects must effectively eliminate discharges of non-storm water into the MS4.

For outdoor areas, exposure reduction generally requires work areas and storage areas to be covered to prevent rain exposure; graded to prevent stormwater run-on and run-off; and protected from the wind so that materials are not dispersed. See Fact Sheet BL-5 (Work and Storage Areas) in Appendix C. If there are storm water discharges from outdoor areas work areas or storage areas,Fact Sheet BL- 6 (Management of Stormwater Discharges) in Appendix C provides practices to prevent discharge of materials from these areas. For interior work surfaces, floor drains and sumps, drain lines, and fire sprinkler test water,exposure reduction generally requires directing the discharge to the sanitary sewer.

See Fact Sheet BL-7 (Management of Non-Stormwater Discharges) in Appendix C. Fact Sheet BL-7 also discusses education for prevention of illicit discharges,which is discussed in more detail below in Section 1.2.2.

4.2.2 Identify the storm drain system using stenciling or signage Storm drain signs and stencils are visible source controls typically placed adjacent to inlets. Posting notices regarding discharge prohibitions at storm drain inlets can prevent waste dumping. Storm drain signage must be provided for all storm water conveyance system inlets and catch basins within the www.sandiegocounty.gov/stormwater 4-3 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects project area. Storm drain signage may include concrete stamping,concrete painting,placards,or other methods approved by the County.A stenciling template used by the County is attached in the "Storm Drain Signage" section of Fact Sheet BL-7 in Appendix C. This template may be modified and used as educational pieces promoting improved water quality.

In addition to storm drain signage, the "Educational BMW Signage" section of Fact Sheet BL-7 encourages applicants to post temporary BMP signage to alert contractors during construction that a permanent BMP has been completed and to ensure it does not get disturbed during subsequent grading and building construction activities.Developments with model homes are encouraged to place educational signage to provide future homeowners a description of the benefits and responsibilities of the BMPs constructed on their property.Interpretive BMP signage provides permanent educational signage for the public to detail how BMPs benefit the local waterways, and may include prohibitive language (with graphical icons) regarding illegal dumping at trailheads, parks, building entrances, and public access points along channels and creeks within the project area.

4.2.3 Protect outdoor material storage areas from rainfall, run-on, runoff, and wind dispersal
Materials with the potential to pollute storm water runoff must be stored in a manner that prevents contact with rainfall and storm water runoff.All development projects must incorporate the following structural or pollutant control BMPs for outdoor material storage areas, as applicable and feasible:
• Storage areas must be paved and sufficiently impervious to contain leaks and spills, where necessary.
• The storage area must be sloped towards a sump or another equivalent measure that is effective to contain spills.
• Runoff from downspouts/roofs must be directed away from storage areas. • The storage area must have a roof or awning that extends beyond the storage area to minimize collection of storm water within the secondary containment area. A manufactured storage shed may be used for small containers.
• Use other methods approved by the County.

See Fact Sheet BL-5 (Work and Storage Areas) in Appendix C for more information.

4.2.4 Protect materials stored in outdoor work areas from rainfall, run- on, runoff, and wind dispersal
Outdoor work areas have an elevated potential for pollutant loading and spills. All development projects must include the following structural or pollutant control BMPs for any outdoor work areas with potential for pollutant generation, as applicable and feasible:
• Create an impermeable surface such as concrete or asphalt, or a prefabricated metal drip pan, depending on the size needed to protect the materials.
• Cover the area with a roof or other acceptable cover. • Berm the perimeter of the area to prevent water from adjacent areas from flowing on to the surface of the work area.
www.sandiegocounty.gov/stormwater 4-4 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects • Directly connect runoff to sanitary sewer or other specialized containment system(s), as needed and where feasible. This allows the more highly concentrated pollutants from these areas to receive special treatment that removes particular constituents. Approval for this connection must be obtained from the appropriate sanitary sewer agency. • Locate the work area away from storm drains or catch basins. • Use other methods approved by the County.

See Fact Sheets BL-5 (Work and Storage Areas) and BL-6 (Management of Stormwater Discharges) in Appendix C for more information.

4.2.5 Protect trash storage areas from rainfall, run-on, runoff, and wind dispersal
Storm water runoff from areas where trash is stored or disposed of can be polluted. In addition,loose trash and debris can be easily transported by water or wind into nearby storm drain inlets, channels, or creeks.All development projects must include the following structural or pollutant control BMPs, as applicable:
• Design trash container areas so that drainage from adjoining roofs and pavement is diverted around the area(s) to avoid run-on. This can include berming or grading the waste handling area to prevent run-on of storm water.
• Ensure trash container areas are screened or walled to prevent offsite transport of trash. • Provide roofs,awnings,or attached lids on all trash containers to minimize direct precipitation and prevent rainfall from entering containers.
• Locate storm drains away from immediate vicinity of the trash storage area and vice versa. • Post signs on all dumpsters informing users that hazardous material are not to be disposed. • Use other methods approved by the County.

See Fact Sheets BL-5 (Work and Storage Areas) and BL-6 (Management of Stormwater Discharges) in Appendix C for more information.

4.2.6 Use any additional BMPs determined to be necessary by the County to minimize pollutant generation at each project site At its discretion, the County may determine that additional on-site controls are necessary to minimize pollutant generation. These determinations will be made on a project-specific basis. Appendix C provides guidance on permanent controls that are applicable at a project site based on potential sources of runoff pollutants at the project site. Applicants must implement all applicable and feasible source control BMPs listed in Appendix C.
www.sandiegocounty.gov/stormwater 4-5 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects

4.3 Site Design (SD) BMP Requirements
Site design BMPs (also referred to as LID BMPs)are intended to reduce the rate and volume of storm water runoff and associated pollutant loads by minimizing surface soil compaction, reducing impervious surfaces, or providing flow pathways that are "disconnected" from the storm drain system, such as by routing flow over pervious surfaces. Site design BMPs may incorporate interception,storage,evaporation,evapotranspiration,infiltration,and/or filtration processes to retain and/or treat pollutants in storm water before it is discharged from a site.

Applicants are referred to the County of San Diego LID Handbook for additional guidance and information on the incorporation of low impact design features in the design of projects. Appendix K (Guidance for Green Infrastructure) provides additional guidance for implementing green street and other sustainable project features and types.

Appendix C also provides the following fact sheets to assist project applicants with designing BMPs to meet Site Design requirements:
• BL-1 —Existing Natural Site Features
• BL-2—Outdoor Impervious Areas
• BL-3—Rooftop Areas
• BL-4—Landscaped Areas
In addition,Appendix E also provides the following fact sheets to assist applicants in Design Capture Volume (DCV) reduction using Enhanced Site Design BMPs:
• SD-A—Tree Wells
• SD-B—Impervious Area Dispersion
• SD-C—Green Roofs
• SD-D—Permeable Pavement (Site Design BMP)
• SD-E—Rain Barrels; and
• SD-F—Amended Soil
The County strongly encourages applicants to utilize these resources to inform the design and construction of low impact design and sustainable infrastructure features for their projects. In addition to generally being environmentally preferable, incorporation of these features can be significantly less expensive than traditional structural approaches, both for construction and ongoing maintenance. Incorporating many of these features may also reduce the sizing requirements for Structural BMPs.

Implementation of Enhanced Site Design BMPs may result in quantifiable reductions in the site's DCV (refer to Appendix B.1);however, failure to meet the minimum thresholds for DCV reductions does not eliminate requirements to implement applicable Site Design BMPs.All applicable and feasible Site Design BMPs must be implemented to the maximum extent practicable. Additionally, implementation of Significant Site Design BMPs (SSD-BMPs) such as Tree Wells and Impervious Area Dispersion when designed to meet flow control per Fact Sheets SD-A and SD-B, respectfully may result in quantifiable hydromodification flow control benefits; refer to Section 6.1 and Appendix

1.1. www.sandiegocounty.gov/stormwater 4-6 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects Per MS4 Permit Provision E.3.a.(3) and WO Section 67.811(a)(5), site design BMPs listed below in 4.3.1 to 4.3.8 must be applied to all development projects as applicable and feasible for the project site and project conditions.

How to comply: Projects must comply with this requirement by using all of the site design BMPs listed in this section that are applicable and practicable to their project type and site conditions.

Applicability of a given site design BMP should be determined based on project type, soil conditions, presence of natural features (e.g. streams),and presence of site features (e.g.parking areas).Applicants must provide an explanation for any site design BMP they do not consider to be applicable and feasible.

Site plans must identify site design BMPs and provide adequate supporting detail to ensure their effective implementation.Table 1 "Baseline BMPs for Existing and Proposed Site Features" which is part of both the Standard SWQMP and the PDP SWQMP listed in Appendix A, should be used to document compliance with site design BMP requirements_Table 1 applies to all development projects,

4.3.1 Maintain natural drainage pathways and hydrologic features ❑ Maintain or restore natural storage reservoirs and drainage corridors (including topographic depressions, areas of permeable soils,natural swales,and ephemeral and intermittent streams) ❑ Buffer zones for natural water bodies (where buffer zones are technically infeasible, require project applicant to include other buffers such as trees, access restrictions, etc.) During the site assessment, natural
drainages must be identified along with their �. connection to creeks or streams, if any. [4Ttk Schack Natural drainages offer a benefit to storm `' ._ water management as the soils and habitat
already function as a natural filtering or .'ter f irk* infiltrating swale. When determining the .' development footprint of the site, altering
natural drainages should be avoided. ByAll
providing a development envelope set back •.,�:~ lr �,f from natural drainages, the drainage can
retain some water quality benefits to the ~
watershed. In some situations, site
constraints,regulations,economics,or other
factors may not allow avoidance of
drainages and sensitive areas. Projects proposing to dredge or fill materials in Waters of the U.S. must obtain Clean Water Act Section 401 Water Quality Certification. Projects proposing to dredge or fill waters of the State must obtain waste discharge requirements. Both the 401 Certification and the Waste Discharge Requirements are administered by the San Diego Water Board.

A setback of 50-200 feet is recommended for development proposed adjacent to Waters of the U.S depending on the type of Water of the U.S. For further guidance, refer to the County of San Diego Guidelines for Determining Significance and Report Format and Content Requirements Biological Resources last revised in September 15, 2010. This document can be found at http://www.sandiegocounty.gov/content/dam/sdc/pds/ProjectPlanning/docs/Biological Guideli nes. df.

Projects can maintain these features into a project by implementing the following planning and design phase techniques:
www.sandiegocounty.gov/stormwater 4-7 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects • Evaluate surface drainage and topography in considering selection of Site Design BMPs that will be most beneficial for a given project site. Where feasible, maintain topographic depressions for infiltration.
• Optimize the existing site layout and reduce the need for grading. Where possible, conform the site layout along natural landforms,avoid grading and disturbance of vegetation and soils, and replicate the site's natural drainage patterns. Integrating existing drainage patterns into the site plan will help maintain the site's predevelopment hydrologic function and may reduce construction costs.
• Preserve existing drainage paths and depressions to maintain the time of concentration and infiltration rates of runoff, and decrease peak flow.
• Do not locate structural BMPs in buffer zones if a State or Federal resource agency (SDRWQCB, California Department of Fish and Wildlife; U.S. Army Corps of Engineers, etc.) prohibits maintenance or activity in the area.

See Fact Sheet BL-1 (Existing Natural Site Features) in Appendix C for more information.

4.3.2 Conserve natural areas, soils and vegetation
❑ Conserve natural areas 44.` development Envelope within the project
footprint including
existing trees, other ' .-
vegetation, and soils '
To enhance a site's ability to lit
r`
support source control and
reduce runoff, the
conservation and restoration of
natural areas must be
considered in the site design ,,k.
`process. By conserving or
,''
restoring the natural drainage
features, natural processes are
able to intercept storm water,
thereby reducing redi the amount """"-d O.J,
of runoff.

The upper soil layers of a natural area contain organic material, soil biota, vegetation, and a configuration favorable for storing and slowly conveying storm water and establishing or restoring vegetation to stabilize the site after construction. The canopy of existing native trees and shrubs also provide a water conservation benefit by intercepting rain water before it hits the ground. By minimizing disturbances in these areas, natural processes are able to intercept storm water,providing a water quality benefit. By concentrating development in the least environmentally sensitive areas of the site and set back from natural areas, storm water runoff is reduced,water quality can be improved, environmental impacts can be decreased, and many of the site's most attractive native landscape features can be retained. In some situations, site constraints, regulations, economics, or other factors may not allow avoidance of all sensitive areas on a project site. Project applicant must consult the County for specific requirements for mitigation of removal of sensitive areas. www.sandiegocounty.gov/stormwater 4-8 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects Projects can incorporate BMPs SD-G (Conserve Natural Features) and SD-H (Buffers) in Fact Sheet BL-1 in Appendix C by implementing the following planning and design phase techniques:
• Identify areas most suitable for development, and areas that should be left undisturbed.

Additionally,disturbance may be reduced by increasing building density and increasing height, if possible.
• Cluster development on the least-sensitive portions of a site while leaving the remaining land in a natural undisturbed condition.

LEAST SENSITIVE 1. AREAS DEVOID OF VEGETATION, INCLUDING

PREVIOUSLY GRADED AREAS AND AGRICULTURAL FIELDS

2. AREAS OF NON-NATIVE VEGETATION, DISTURBED HABITATS

AND EUCALYPTUS WOODLANDS WHERE RECEIVING WATERS

ARE NOT PRESENT

3. AREAS OF CHAMISE OR MIXED CHAPARRAL,

AND NON-NATIVE GRASSLANDS

4. AREAS CONTAINING COASTAL SCRUB COMMUNITIES

5. ALL OTHER UPLAND COMMUNITIES

6. OCCUPIED HABITAT OF SENSITIVE SPECIES AND ALL WETLANDS MOST SENSITIVE (AS BOTH ARE DEFINED BY THE LOCAL JURISDICTION) • Avoid areas with thick, undisturbed vegetation. Soils in these areas have a much higher capacity to store and infiltrate runoff than disturbed soils, and reestablishment of a mature vegetative community can take decades. Vegetative cover can also provide additional volume storage of rainfall by retaining water on the surfaces of leaves, branches, and trunks of trees during and after storm events.
• Preserve trees,especially native trees and shrubs,and identify locations for planting additional native or drought tolerant trees and large shrubs. Refer to Appendix E for additional guidance on implementing SD-A Tree Wells as a Site Design BMP.
• In areas of disturbance, topsoil should be removed before construction and replaced after the project is completed. When handled carefully, such an approach limits the disturbance to native soils and reduces the need for additional (purchased) topsoil during later phases. • Avoid sensitive areas,such as wetlands,biological open space areas,biological mitigation sites, streams, floodplains, or particular vegetation communities, such as coastal sage scrub and intact forest. Also, avoid areas that are habitat for sensitive plants and animals, particularly those that are State or federally listed as endangered,threatened,or rare.Development in these areas is often restricted by federal, state and local laws.

See Fact Sheet BL-1 (Existing Natural Site Features) in Appendix C for more information.

4.3.3 Minimize impervious area
❑ Construct streets, sidewalks or parking lots aisles to the minimum widths necessary,provided public safety is not compromised.
❑ Minimize the impervious footprint of the project.
www.sandiegocounty.gov/stormwater 4-9 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects One of the principal causes of environmental impacts by development is the creation of impervious surfaces. Imperviousness links urban land development to degradation of aquatic ecosystems in two ways:
• First,the combination of paved surfaces and piped runoff efficiently collects urban pollutants and transports them,in suspended or dissolved form,to surface waters.These pollutants may originate as airborne dust,be washed from the atmosphere during rains, or may be generated by automobiles and outdoor work activities.
• Second,increased peak flows and runoff durations typically cause erosion of stream banks and beds,transport of fine sediments,and disruption of aquatic habitat.Measures taken to control stream erosion, such as hardening banks with riprap or concrete, may permanently eliminate habitat.

Impervious cover can be minimized Preserve Existing Trees Clustered Buildings
through identification of the
smallest possible land area that can
be practically impacted or disturbed Narrow Street during site development. Reducing
impervious surfaces retains the ..
permeability of the project site,
allowing natural processes to filter �� "r and reduce sources of pollution.

Projects can conserve these features,
by implementing the following 4 #
Fr�nrg f+�igting
planning and design phase InfillratbnAr-2,m techniques as applicable and Shared DrW& ay feasible:
• Decrease the building footprint through the design of compact and taller structures when allowed by County zoning and design standards, and provided public safety is not compromised.
• Construct walkways, trails, patios, overflow parking lots, alleys, and other low-traffic areas with permeable surfaces.Refer to Appendix E for additional guidance on implementing SD-D Permeable Pavement as a Site Design BMP.
• Construct streets, sidewalks and parking lot aisles to the minimum widths necessary,provided that public safety and alternative transportation (e.g. pedestrians,bikes) are not compromised. • Consider the implementation of shared parking lots and driveways where possible. • Landscaped area in the center of a cul-de-sac can reduce impervious area depending on configuration. Design of a landscaped cul-de-sac must be coordinated with fire department personnel to accommodate turning radii and other operational needs. • Design smaller parking lots with fewer stalls, smaller stalls, and more efficient lanes. • Design parking indoors or underground.
• Minimize the use of impervious surfaces in the landscape design. www.sandiegocounty.gov/stormwater 4-10 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects See Fact Sheets BL-2 (Outdoor Impervious Area), BL-3 (Rooftop Areas), and BL-4 (Landscaped Areas) in Appendix C for more information.

In addition, the following fact sheets provided in Appendix E describe ways to reduce impervious areas:
• SD-B—Impervious Area Dispersion;
• SD-C—Green Roofs; and
• SD-D—Permeable Pavement (Site Design).

4.3.4 Minimize soil compaction
❑ Minimize soil compaction in landscaped areas
The upper soil layers contain organic material, soil biota,and a configuration favorable for storing and slowly conveying storm water down gradient. By protecting native soils and vegetation in appropriate areas during clearing and grading the site can retain some of its existing beneficial hydrologic function.

Soil compaction resulting from the movement of heavy construction equipment can reduce soil infiltration rates. It is important to recognize that areas adjacent to and under building foundations, roads and manufactured slopes must be compacted with minimum soil density requirements in compliance with County building and grading ordinances.

Projects can incorporate BMP SD-G (Conserve Natural Areas) and SD-K (Sustainable Landscaping) in Fact Sheets BL-1 and BL-4, respectively in Appendix C by implementing the following planning and design phase techniques as applicable and feasible:
• Avoid disturbance in planned green space and proposed landscaped areas where feasible.

Areas that are planned for retaining their beneficial hydrological function should be protected during the grading and construction phase so that vehicles and construction equipment do not intrude and inadvertently compact the area.
• In areas planned for landscaping where compaction cannot be avoided, re-till the soil surface to allow for better infiltration capacity. Soil amendments are recommended and may be necessary to increase permeability and organic content. Soil stability,density requirements,and other geotechnical considerations associated with soil compaction must be reviewed by a qualified landscape architect or licensed geotechnical, civil or other professional engineer.

Refer to fact sheet SD-F in Appendix E for additional guidance on implementing amended soils within the project footprint.

See Fact Sheets BL-1 (Existing Natural Site Features) and BL-4 (Landscaped Areas) in Appendix C for more information.

4.3.5 Disperse impervious areas
❑ Disconnect impervious surfaces through distributed pervious areas. ❑ Design and construct landscaped or other pervious areas to effectively receive and infiltrate, retain and/or treat runoff from impervious areas prior to discharging to the MS4 Impervious area dispersion (dispersion) refers to the practice of disconnecting impervious areas from directly draining to the storm drain system by routing runoff from impervious areas such as rooftops, www.sandiegocounty.gov/stormwater 4-11 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects walkways, and driveways onto the surface of adjacent pervious areas. The intent is to slow runoff discharges, and to reduce volumes while achieving incidental treatment. Volume reduction from dispersion is dependent on the infiltration characteristics of the pervious area and the amount of impervious area draining to the pervious area. Treatment is achieved through filtration, shallow sedimentation, sorption,infiltration, evapotranspiration, biochemical processes and plant uptake.

The effects of imperviousness can be mitigated by disconnecting impervious areas from the drainage system and by encouraging detention and retention of runoff near the point where it is generated.

Detention and retention of runoff reduces peak flows and volumes and allows pollutants to settle out or adhere to soils before they can be transported downstream.Disconnection practices may be applied in almost any location, but impervious surfaces must discharge into a suitable receiving area for the practices to be effective. Information gathered during the site assessment will help determine appropriate receiving areas.

Project designs should direct runoff from impervious areas to adjacent landscaping areas that have higher potential for infiltration and surface water storage. This will limit the amount of runoff generated, and therefore the size of the mitigation BMPs downstream. The design, including consideration of slopes and soils, must reflect a reasonable expectation that runoff will soak into the soil and produce no runoff of the DCV. On hillside sites,drainage from upper areas may be collected in conventional catch basins and piped to landscaped areas that have higher potential for infiltration.

Or use low retaining walls to create terraces that can accommodate BMPs.

Sheet Flow �
to Street
Curb/Gutter Sheet Flow
Collets taTurfar
Runoff Groundcover
Stormwater
Concentrated IriRl trates
Pollutants into the Soil
Carried to
Outfall
www.sandiegocounty.gov/stormwater 4-12 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects Projects can incorporate impervious area dispersion through the following planning and design phase techniques:
• Implement design criteria and considerations listed in the impervious area dispersion fact sheet (SD-B) presented in Appendix E.
• Drain rooftops into adjacent landscape areas.
• Drain impervious parking lots, sidewalks,walkways, trails, and patios into adjacent landscape areas.
• Reduce or eliminate curb and gutters or place curb openings from roadway sections, thus allowing roadway runoff to drain to adjacent pervious areas. • Replace curbs and gutters with roadside vegetated swales or place curb openings and direct runoff from the paved street or parking areas to adjacent LID facilities. This can reduce the overall capital cost of the site development while improving the storm water quantity and quality issues and the site's aesthetics.
• Plan site layout and grading to allow for runoff from impervious surfaces to be directed into distributed permeable areas such as turf,landscaped or permeable recreational areas,medians, parking islands,planter boxes, etc.
• Detain and retain runoff throughout the site. On flatter sites, landscaped areas can be interspersed among the buildings and pavement areas. On hillside sites, drainage from upper areas may be collected in conventional catch basins and conveyed to landscaped areas in lower areas of the site.
• Pervious area that receives run on from impervious surfaces should have a minimum width of 10 feet and a maximum slope of 5%.

See Fact Sheets BL-2 (Outdoor Impervious Areas), BL-3 (Rooftop Areas) and BL-4 (Landscaped Areas) in Appendix C for more information.

In addition, the following fact sheet in Appendix E describes ways to reduce the impact of runoff from impervious areas:
• SD-B- Impervious area dispersion

4.3.6 Collect runoff
❑ Use small collection strategies located at,or as close to as possible to the sources (i.e. the point where storm water initially meets the ground) to minimize the transport of runoff and pollutants to the MS4 and receiving waters
❑ Use permeable material for projects with low traffic areas and appropriate soil conditions.

Refer to Appendix E for additional guidance on implementing SD-D Permeable Pavement as a Site Design BMP.

Distributed control of storm water runoff from the site can be accomplished by applying small collection techniques (e.g. SD-C Green Roofs in Appendix E), or integrated management practices, on small sub-catchments or on residential lots. Small collection techniques foster opportunities to maintain the natural hydrology provide a much greater range of control practices.Integration of storm water management into landscape design and natural features of the site,reduce site development and www.sandiegocounty.gov/stormwater 4-13 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects long-term maintenance costs, and provide redundancy if one technique fails. On flatter sites, it typically works best to intersperse landscaped areas and integrate small scale retention practices among the buildings and paving.

Permeable pavements contain small voids that allow water to pass through to a gravel base. They come in a variety of forms; they may be a modular paving system (concrete pavers, grass-pave, or gravel-pave) or poured in place pavement (porous concrete, permeable asphalt). Project applicants should identify locations where permeable pavements could be substituted for impervious concrete or asphalt paving.In areas where infiltration is not appropriate,permeable paving systems can be fitted with an under drain to allow filtration,storage,and evaporation,prior to drainage into the storm drain system.

Projects can incorporate runoff collection by implementing the following planning and design phase techniques:
• Implementing distributed small collection techniques to collect and retain runoff (see SD-E Rain Barrels in Appendix E)
• Installing permeable pavements (see SD-D Permeable Pavement in Appendix E) See Fact Sheets BL-2 (Outdoor Impervious Areas) and BL-3 (Rooftop Areas)in Appendix C for more information.

4.3.7 Landscape with native or drought tolerant species In accordance with the County's Watershed Protection Ordinance and Water Conservation in Landscaping Ordinances, applicants should select a landscape design and plant palette that minimizes required resources (irrigation, fertilizers and pesticides). Native plants require less fertilizer and pesticide use because they are already adapted to local rainfall patterns and soils conditions. Plants should be selected to be drought tolerant and to not require watering after establishment(2 to 3 years).

After plants are established, watering should only be required during prolonged dry periods. Final selection of plant material should be made by a landscape architect experienced with LID techniques.

Microclimates vary significantly throughout the region and consulting County resources (i.e., Water Efficient Landscape Design Manual)will help to select plant material suitable for a specific geographic location.

See Fact Sheet BL-4 (Landscaped Areas) in Appendix C for more information.

Note.Forpr jects with bioretention facilities, applicants should consult Fact Sbeet E3 in Appendix F for a list of loan water use plants able to withstand up to 96 bours of inundation. s Available online at https://www.sandiegocounty.gov/content/sdc/pds/LandscapeOrdinance.html 6 Available online at https://www.sandiegocounty.gov/content/sdc/pds/LandscapeOrdinance.html.) www.sandiegocounty.gov/stormwater 4-14 Effective September 15,2020

Chapter 4: Source Control and Site Design Requirements for All Development Projects

4.3.8 Harvest and use precipitation Photograph Coirresy of AndSohitions,Inc.

Harvest and use BMPs capture and store storm
water runoff for later use. Harvest and use can be
applied at smaller scales (Standard Projects) using
rain barrels or at larger scales (PDPs) using
cisterns. This harvest and use technique has been
successful in reducing runoff discharged to the
storm drain system conserving potable water and
recharging groundwater.

Rain barrels are aboveground storage vessels that �,y capture runoff from roof downspouts during rain
events and detain that runoff for later reuse for
irrigating landscaped areas.The temporary storage
of roof runoff reduces the runoff volume from a
property and may reduce the peak runoff velocity
for small,frequently occurring storms.In addition,
by reducing the amount of storm water runoff that i flows overland into a storm water conveyance
system (storm drain inlets and drain pipes), less pollutants are transported through the conveyance system into local creeks and the ocean. The reuse of the detained water for irrigation purposes leads to the conservation of potable water and the recharge of groundwater. SD-E fact sheet (Rain Barrels) in Appendix E provides additional detail for designing Harvest and Use BMPs. Projects can incorporate BMP SD-E by installing rain barrels or cisterns, as applicable.

Note:Harvest and use BMPs proposed for indoor uses may require additional County approvals. Applicants should consult with staff for specific requirements.
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Building & Grounds Maintenance SC-41
Description
Stormwater runoff from building and grounds Objectives maintenance activities can be contaminated ■ Cover
with toxic hydrocarbons in solvents,fertilizers ■ Contain and pesticides, suspended solids,heavy metals, . Educate abnormal pH, and oils and greases. Utilizing
the protocols in this fact sheet will prevent or ■ Reduce/Minimize reduce the discharge of pollutants to ■ Product Substitution stormwater from building and grounds
maintenance activities by washing and cleaning Targeted Constituents up with as little water as possible,following Sediment good landscape management practices, Nutrients ✓ preventing and cleaning up spills immediately,
keeping debris from entering the storm drains, Trash
and maintaining the stormwater collection Metals ✓ system.

Bacteria
Approach Oil and Grease
Reduce potential for pollutant discharge Organics
through source control pollution prevention
and BMP implementation. Successful Minimum BMPs Covered implementation depends on effective training Good Housekeeping ✓ of employees on applicable BMPs and general
pollution prevention strategies and objectives. � - Preventative
General Pollution Prevention Protocols , Maintenance Spill and Leak
❑ Switch to non-toxic chemicals for Prevention and ✓ maintenance to the maximum extent - Response
possible. Material Handling& ✓
Waste Management
❑ Choose cleaning agents that can be Erosion and Sediment recycled. Controls
Employee Training ✓
❑ Encourage proper lawn management and 0 Program
landscaping,including use of native Quality Assurance vegetation. V�V Record Keeping '�
❑ Encourage use of Integrated Pest
Management techniques for pest control.
❑ Encourage proper onsite recycling of yard
trimmings.
❑ Recycle residual paints,solvents,lumber,
and other material as much as possible. CASQA

CALIFORNIA STORMWATER

QUALITY ASSOCIATION-
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Building & Grounds Maintenance SC-41
❑ Clean work areas at the end of each work shift using dry cleaning methods such as sweeping and vacuuming.
=v Good Housekeeping
Pressure Washing of Buildings,Rooftops, and Other Large Objects ❑ In situations where soaps or detergents are used and the surrounding area is paved, pressure washers must use a water collection device that enables collection of wash water and associated solids.A sump pump,wet vacuum or similarly effective device must be used to collect the runoff and loose materials.The collected runoff and solids must be disposed of properly.
❑ If soaps or detergents are not used, and the surrounding area is paved,wash runoff does not have to be collected but must be screened. Pressure washers must use filter fabric or some other type of screen on the ground and/or in the catch basin to trap the particles in wash water runoff.
❑ If you are pressure washing on a grassed area(with or without soap),runoff must be dispersed as sheet flow as much as possible,rather than as a concentrated stream.

The wash runoff must remain on the grass and not drain to pavement.

Landscaping Activities
❑ Dispose of grass clippings,leaves, sticks,or other collected vegetation as garbage,or by composting. Do not dispose of collected vegetation into waterways or storm drainage systems.
❑ Use mulch or other erosion control measures on exposed soils. See also SC-40, Contaminated and Erodible Areas,for more information.

Building Repair,Remodeling, and Construction
❑ Do not dump any toxic substance or liquid waste on the pavement,the ground,or toward a storm drain.
❑ Use ground or drop cloths underneath outdoor painting, scraping, and sandblasting work, and properly dispose of collected material daily. ❑ Use a ground cloth or oversized tub for activities such as paint mixing and tool cleaning.
❑ Clean paintbrushes and tools covered with water-based paints in sinks connected to sanitary sewers or in portable containers that can be dumped into a sanitary sewer drain. Brushes and tools covered with non-water-based paints,finishes, or other materials must be cleaned in a manner that enables collection of used solvents (e.g., paint thinner,turpentine,etc.)for recycling or proper disposal. ❑ Use a storm drain cover,filter fabric,or similarly effective runoff control mechanism if dust,grit,wash water,or other pollutants may escape the work area and enter a catch basin. This is particularly necessary on rainy days.The containment device(s) must be in place at the beginning of the work day,and accumulated dirty runoff and September 2014 California Stormwater BMP Handbook 2 of 6 Industrial and Commercial
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Building & Grounds Maintenance SC-41
solids must be collected and disposed of before removing the containment device(s) at the end of the work day.
❑ If you need to de-water an excavation site,you may need to filter the water before discharging to a catch basin or off-site.If directed off-site,you should direct the water through hay bales and filter fabric or use other sediment filters or traps. ❑ Store toxic material under cover during precipitation events and when not in use.A cover would include tarps or other temporary cover material.

Mowing, Trimming, and Planting
❑ Dispose of leaves,sticks, or other collected vegetation as garbage,by composting or at a permitted landfill. Do not dispose of collected vegetation into waterways or storm drainage systems.
❑ Use mulch or other erosion control measures when soils are exposed. ❑ Place temporarily stockpiled material away from watercourses and drain inlets, and berm or cover stockpiles to prevent material releases to the storm drain system. ❑ Consider an alternative approach when bailing out muddy water: do not put it in the storm drain;pour over landscaped areas.
❑ Use hand weeding where practical.

Fertilizer and Pesticide Management
❑ Do not use pesticides if rain is expected.
❑ Do not mix or prepare pesticides for application near storm drains. ❑ Use the minimum amount needed for the job.
❑ Calibrate fertilizer distributors to avoid excessive application. ❑ Employ techniques to minimize off-target application(e.g., spray drift) of pesticides, including consideration of alternative application techniques. ❑ Apply pesticides only when wind speeds are low.
❑ Fertilizers should be worked into the soil rather than dumped or broadcast onto the surface.
❑ Irrigate slowly to prevent runoff and then only as much as is needed. ❑ Clean pavement and sidewalk if fertilizer is spilled on these surfaces before applying irrigation water.

Inspection
❑ Inspect irrigation system periodically to ensure that the right amount of water is being applied and that excessive runoff is not occurring. Minimize excess watering and repair leaks in the irrigation system as soon as they are observed.

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Building & Grounds Maintenance SC-41
(D
Spill Response and Prevention Procedures
❑ Keep your Spill Prevention Control and Countermeasure (SPCC) Plan up-to-date. ❑ Place a stockpile of spill cleanup materials, such as brooms, dustpans, and vacuum sweepers (if desired)near the storage area where it will be readily accessible. ❑ Have employees trained in spill containment and cleanup present during the loading/unloading of dangerous wastes,liquid chemicals, or other materials. ❑ Familiarize employees with the Spill Prevention Control and Countermeasure Plan. ❑ Clean up spills immediately.
r
Material Handling and Waste Management
❑ Follow all federal, state, and local laws and regulations governing the use, storage, T and disposal of fertilizers and pesticides and training of applicators and pest control advisors.
❑ Use less toxic pesticides that will do the job when applicable. Avoid use of copper- based pesticides if possible.
❑ Dispose of empty pesticide containers according to the instructions on the container label.
❑ Use up the pesticides. Rinse containers, and use rinse water as product. Dispose of unused pesticide as hazardous waste.
❑ Implement storage requirements for pesticide products with guidance from the local fire department and County Agricultural Commissioner. Provide secondary containment for pesticides.

Employee Training Program
❑ Educate and train employees on pesticide use and in pesticide application techniques to prevent pollution.
❑ Train employees and contractors in proper techniques for spill containment and cleanup.
❑ Be sure the frequency of training takes into account the complexity of the operations and the needs of individual staff.

Quality Assurance and Record Keeping
i
❑ Keep accurate logs that document maintenance activities performed and minimum BMP measures implemented.
❑ Keep accurate logs of spill response actions that document what was spilled,how it was cleaned up, and how the waste was disposed.
❑ Establish procedures to complete logs and file them in the central office.

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Building & Grounds Maintenance SC-41
Potential Capital Facility Costs and Operation & Maintenance Requirements
Facilities
❑ Additional capital costs are not anticipated for building and grounds maintenance.

Implementation of the minimum BMPs described above should be conducted as part of regular site operations.

Maintenance
❑ Maintenance activities for the BMPs described above will be minimal, and no additional cost is anticipated.

Supplemental Information
Fire Sprinkler Line Flushing
Site fire sprinkler line flushing may be a source of non-stormwater runoff pollution. The water entering the system is usually potable water,though in some areas it may be non- potable reclaimed wastewater. There are subsequent factors that may drastically reduce the quality of the water in such systems. Black iron pipe is usually used since it is cheaper than potable piping,but it is subject to rusting and results in lower quality water. Initially, the black iron pipe has an oil coating to protect it from rusting between manufacture and installation;this will contaminate the water from the first flush but not from subsequent flushes. Nitrates,poly-phosphates and other corrosion inhibitors, as well as fire suppressants and antifreeze may be added to the sprinkler water system.

Water generally remains in the sprinkler system a long time(typically a year)and between flushes may accumulate iron, manganese,lead, copper,nickel,and zinc. The water generally becomes anoxic and contains living and dead bacteria and breakdown products from chlorination. This may result in a significant BOD problem and the water often smells. Consequently dispose fire sprinkler line flush water into the sanitary sewer.

Do not allow discharge to storm drain or infiltration due to potential high levels of pollutants in fire sprinkler line water.

References and Resources
City of Seattle, Seattle Public Utilities Department of Planning and Development, 2009.

Stormwater Manual Vol. 1 Source Control Technical Requirements Manual.

Kennedy/Jenks Consultants, 2007. The Truckee Meadows Industrial and Commercial Storm Water Best Management Practices Handbook. Available online at:
http:/l www.ciVofsparks.us Zsites/default/files/assets/documents/env- control/construction/TM-I-C BMP Handbook 2-o7-final.pdf.

Orange County Stormwater Program, Best Management Practices for Industrial/Commercial Business Activities.Available online at:
http://ocwatersheds.com/documents/bmp/industrialcommercialbusinessesactivities .

Sacramento Stormwater Management Program. Best Management Practices for Industrial Storm Water Pollution Control. Available online at:

September 2014 California Stormwater BMP Handbook 5 of 6 Industrial and Commercial
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Building & Grounds Maintenance SC-41
http://www.msa.saccouniy.net/sactostormwater/documents uides/industrial-BMP- manual.pdf.

US EPA, 1997. Best Management Practices Handbook for Hazardous Waste Containers. Available online at: http://www.epa.gov/region6/6en/h/handbk4_pdf .

Ventura Countywide Stormwater Management Program Clean Business Fact Sheets.

Available online at:
http_// www.vcstormwater.org/documents/programs business/building pdf.

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Drainage System Maintenance SC-44
Description
As a consequence of its function,the Objectives stormwater drainage facilities on site convey ■ Cover stormwater that may contain certain pollutants ■ Contain either to the offsite conveyance system that ■ Educate collects and transports urban runoff and
stormwater,or directly to receiving waters.The ■ Reduce/Minimize protocols in this fact sheet are intended to Targeted Constituents reduce pollutants leaving the site to the offsite Sediment drainage infrastructure or to receiving waters
through proper on-site conveyance system Nutrients ✓ operation and maintenance. The targeted Trash
constituents will vary depending on site
characteristics and operations. Metals
Approach Bacteria ,/
Successful implementation depends on Oil and Grease ✓ effective training of employees on applicable Organics ✓ BMPs and general pollution prevention
strategies and objectives. Minimum BMPs Covered General Pollution Prevention Protocols Good Housekeeping ✓ ❑ Preventative Maintain catch basins,stormwater inlets, 0 ✓ and other stormwater conveyance ------ Maintenance structures on a regular basis to remove Spill and Leak pollutants,reduce high pollutant _ Prevention and ✓ concentrations during the first flush of Response storms,prevent clogging of the downstream Material Handling& conveyance system, restore catch basins' - Waste Management sediment trapping capacity, and ensure the Erosion and Sediment system functions properly hydraulically to - Controls avoid flooding. Employee Training ✓
Program
❑ Develop and follow a site specific drainage Quality Assurance ✓ system maintenance plan that describes -+' Record Keeping maintenance locations,methods,required
equipment,water sources, sediment
collection areas, disposal requirements, and
any other pertinent information.

Good Housekeeping
Illicit Connections and Discharges
❑ Look for evidence of illegal discharges or
illicit connections during routine .
maintenance of conveyance system and
drainage structures:

CALIFORNIA STORMWATER

QUALITY ASSOCIATION-
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Drainage System Maintenance SC-44
✓ Identify evidence of spills such as paints, discoloring, odors, etc. ✓ Record locations of apparent illegal discharges/illicit connections. ✓ Track flows back to potential discharges and conduct aboveground inspections.

This can be done through visual inspection of upgradient manholes or alternate techniques including zinc chloride smoke testing,fluorometric dye testing, physical inspection testing, or television camera inspection. ✓ Eliminate the discharge once the origin of flow is established. ❑ Stencil or demarcate storm drains,where applicable,to prevent illegal disposal of pollutants. Storm drain inlets should have messages such as "Dump No Waste Drains to Stream"or similar stenciled next to them to warn against ignorant or intentional dumping of pollutants into the storm drainage system. ❑ Refer to fact sheet SC-10 Non-Stormwater Discharges for additional information.

Illegal Dumping
❑ Inspect and clean up hot spots and other storm drainage areas regularly where illegal dumping and disposal occurs.
❑ Establish a system for tracking incidents. The system should be designed to identify the following:
✓ Illegal dumping hot spots;
✓ Types and quantities (in some cases) of wastes;
✓ Patterns in time of occurrence(time of day/night, month, or year); ✓ Mode of dumping (abandoned containers, "midnight dumping"from moving vehicles, direct dumping of materials, accidents/spills); and ✓ Responsible parties.
❑ Post"No Dumping"signs in problem areas with a phone number for reporting dumping and disposal. Signs should also indicate fines and penalties for illegal dumping.
❑ Refer to fact sheet SC-10 Non-Stormwater Discharges for additional information.

Preventative Maintenance
Catch Basins/Inlet Structures
❑ Staff should regularly inspect facilities to ensure compliance with the following:
✓ Immediate repair of any deterioration threatening structural integrity. ✓ Cleaning before the sump is 40%full. Catch basins should be cleaned as frequently as needed to meet this standard.

September 2014 California Stormwater BMP Handbook 2 of 7 Industrial and Commercial
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Drainage System Maintenance SC-44
❑ Clean catch basins,storm drain inlets, and other conveyance structures before the wet season to remove sediments and debris accumulated during the summer. ❑ Conduct inspections more frequently during the wet season for problem areas where sediment or trash accumulates more often. Prioritize storm drain inlets; clean and repair as needed.
❑ Keep accurate logs of the number of catch basins cleaned. ❑ Store wastes collected from cleaning activities of the drainage system in appropriate containers or temporary storage sites in a manner that prevents discharge to the storm drain.
❑ Dewater the wastes if necessary with outflow into the sanitary sewer if permitted.

Water should be treated with an appropriate filtering device prior to discharge to the sanitary sewer. If discharge to the sanitary sewer is not allowed,water should be pumped or vacuumed to a tank and properly disposed. Do not dewater near a storm drain or stream.

Storm Drain Conveyance System
❑ Locate reaches of storm drain with deposit problems and develop a flushing schedule that keeps the pipe clear of excessive buildup.
❑ Collect and pump flushed effluent to the sanitary sewer for treatment whenever possible.

Pump Stations
❑ Clean all storm drain pump stations prior to the wet season to remove silt and trash. ❑ Do not allow discharge to reach the storm drain system when cleaning a storm drain pump station or other facility.
❑ Conduct routine maintenance at each pump station.
❑ Inspect, clean, and repair as necessary all outlet structures prior to the wet season.

Open Channel
❑ Modify storm channel characteristics to improve channel hydraulics,increase pollutant removals, and enhance channel/creek aesthetic and habitat value. ❑ Conduct channel modification/improvement in accordance with existing laws. Any person,government agency,or public utility proposing an activity that will change the natural state of any river, stream,or lake in California,must enter into a Steam or Lake Alteration Agreement with the Department of Fish and Wildlife. The developer-applicant should also contact local governments(city,county,special districts),other state agencies (SWRCB, RWQCB,Department of Forestry, Department of Water Resources), and Army Corps of Engineers and USFWS.

Spill Response and Prevention Procedures
❑ Keep your spill prevention control plan up-to-date.

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Drainage System Maintenance SC-44
❑ Investigate all reports of spills, leaks, and/or illegal dumping promptly. ❑ Place a stockpile of spill cleanup materials where it will be readily accessible or at a central location.
❑ Clean up all spills and leaks using"dry"methods(with absorbent materials and/or rags)or dig up, remove, and properly dispose of contaminated soil. acomployee Training Program Educate employees about pollution prevention measures and goals. ❑ Train employees how to properly handle and dispose of waste using the source control BMPs described above.
❑ Train employees and subcontractors in proper hazardous waste management. ❑ Use a training log or similar method to document training. ❑ Ensure that employees are familiar with the site's spill control plan and/or proper spill cleanup procedures.
❑ Have staff involved in detection and removal of illicit connections trained in the following:
✓ OSHA-required Health and Safety Training(29 CFR 1910.120)plus annual refresher training(as needed).
✓ OSHA Confined Space Entry training(Cal-OSHA Confined Space,Title 8 and Federal OSHA 29 CFR 1910.146).
✓ Procedural training(field screening,sampling, smoke/dye testing,TV inspection).

Quality Assurance and Record Keeping
❑ Keep accurate maintenance logs that document minimum BMP activities performed for drainage system maintenance,types and quantities of waste disposed of, and any improvement actions.
❑ Keep accurate logs of spill response actions that document what was spilled,how it was cleaned up, and how the waste was disposed.
❑ Keep accurate logs of illicit connections, illicit discharges, and illegal dumping into the storm drain system including how wastes were cleaned up and disposed. ❑ Establish procedures to complete logs and file them in the central office.

Potential Limitations and Work-Arounds
Provided below are typical limitations and recommended"work-arounds"for drainage system maintenance:

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Drainage System Maintenance SC-44
❑ Clean-up activities may create a slight disturbance for local aquatic species. Access to items and material on private property may be limited. Trade-offs may exist between channel hydraulics and water quality/riparian habitat. If storm channels or basins are recognized as wetlands,many activities,including maintenance, may be subject to regulation and permitting.
✓ Perform all maintenance onsite and do not flush accumulated material downstream to private property or riparian habitats.
❑ Storm drain flushing is most effective in small diameter pipes (36-inch diameter pipe or less, depending on water supply and sediment collection capacity). Other considerations associated with storm drain flushing may include the availability of a water source,finding a downstream area to collect sediments, and liquid/sediment disposal.
✓ Develop and follow a site specific drainage system maintenance plan that describes maintenance locations, methods, required equipment,water sources, sediment collection areas, disposal requirements, and any other pertinent information.
❑ Regulations may include adoption of substantial penalties for illegal dumping and disposal.
✓ Do not dump illegal materials anywhere onsite.
✓ Identify illicit connections, illicit discharge, and illegal dumping. ✓ Cleanup spills immediately and properly dispose of wastes. ❑ Local municipal codes may include sections prohibiting discharge of soil, debris, refuse,hazardous wastes, and other pollutants into the sanitary sewer system. ✓ Collect all materials and pollutants accumulated in drainage system and dispose of according to local regulations.
✓ Install debris excluders in areas with a trash TMDL.

Potential Capital Facility Costs and Operation & Maintenance Requirements
Facilities
❑ Capital costs will vary substantially depending on the size of the facility and characteristics of the drainage system. Significant capital costs may be associated with purchasing water trucks,vacuum trucks, and any other necessary cleaning equipment or improving the drainage infrastructure to reduce the potential. ❑ Developing and implementing a site specific drainage system maintenance plan will require additional capital if a similar program is not already in place.

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Drainage System Maintenance SC-44
Maintenance
❑ Two-person teams may be required to clean catch basins with vactor trucks. ❑ Teams of at least two people plus administrative personnel are required to identify illicit discharges, depending on the complexity of the storm sewer system. ❑ Arrangements must be made for proper disposal of collected wastes. ❑ Technical staff are required to detect and investigate illegal dumping violations. ❑ Methods used for illicit connection detection(smoke testing, dye testing,visual inspection, and flow monitoring)can be costly and time-consuming. Site-specific factors,such as the level of impervious area,the density and ages of buildings, and type of land use will determine the level of investigation necessary.

Supplemental Information
Storm Drain Flushing
Flushing is a common maintenance activity used to improve pipe hydraulics and to remove pollutants in storm drainage systems. Flushing may be designed to hydraulically convey accumulated material to strategic locations,such as an open channel, another point where flushing will be initiated, or the sanitary sewer and the treatment facilities, thus preventing re-suspension and overflow of a portion of the solids during storm events. Flushing prevents"plug flow"discharges of concentrated pollutant loadings and sediments. Deposits can hinder the designed conveyance capacity of the storm drain system and potentially cause backwater conditions in severe cases of clogging.

Storm drain flushing usually takes place along segments of pipe with grades that are too flat to maintain adequate velocity to keep particles in suspension. An upstream manhole is selected to place an inflatable device that temporarily plugs the pipe. Further upstream,water is pumped into the line to create a flushing wave. When the upstream reach of pipe is sufficiently full to cause a flushing wave,the inflated device is rapidly deflated with the assistance of a vacuum pump, thereby releasing the backed up water and resulting in the cleaning of the storm drain segment.

To further reduce impacts of stormwater pollution, a second inflatable device placed well downstream may be used to recollect the water after the force of the flushing wave has dissipated. A pump may then be used to transfer the water and accumulated material to the sanitary sewer for treatment. In some cases, an interceptor structure may be more practical or required to recollect the flushed waters.

It has been found that cleansing efficiency of periodic flush waves is dependent upon flush volume,flush discharge rate, sewer slope, sewer length,sewer flow rate, sewer diameter, and population density. As a rule of thumb,the length of line to be flushed should not exceed 700 feet. At this maximum recommended length,the percent removal efficiency ranges between 65-75%for organics and 55-65%for dry weather grit/inorganic material. The percent removal efficiency drops rapidly beyond that.

Water is commonly supplied by a water truck,but fire hydrants can also supply water.

To make the best use of water,it is recommended that reclaimed water be used if allowed or that fire hydrant line flushing coincide with storm sewer flushing.

September 2014 California Stormwater BMP Handbook 6 of 7 Industrial and Commercial
www.casga.org

Drainage System Maintenance SC-44
References and Resources
City of Seattle, Seattle Public Utilities Department of Planning and Development, 2009.

Stormwater Manual Vol. 1 Source Control Technical Requirements Manual.

Knox County Tennessee Stormwater Management Manual Chapter 5 Drainage System Maintenance, 2oo8. Available online at:
http://www.knoxcounty.org/stormwater/manual/Volume%2o1/knoxco swmm vi cha p. jan20o8.pdf.

US EPA. Storm Drain System Cleaning, 2012. Available online at:
http://cfpub.epa.gov/npdes/stormwater/menuofbmps/index.cfm?action=browse&Rbut ton=detail&bmp=lot.

September 2014 California Stormwater BMP Handbook 7 of 7 Industrial and Commercial
www.casqa.org

Appendix C — Structural Control BMPs
11 1205 Melrose Way
March 2021

BF-1 Biofiltration
E.14 BF-1 Biofiltration
MS4 Permit Category
Biofiltration
t + Manual Category
Biofiltration
Applicable Performance
Standard
�. Pollutant Control
Flow Control
Primary Benefits
Treatment
ocation d treet and o an Avenue an ie o California Volume Reduction (Incidental) Peak Flow Attenuation (Optional)
Description
Biofiltration (Bioretention with underdrain) facilities are vegetated surface water systems that filter water through vegetation, and soil or engineered media prior to discharge via underdrain or overflow to the downstream conveyance system. Bioretention with underdrain facilities are commonly incorporated into the site within parking lot landscaping,along roadsides,and in open spaces.Because these types of facilities have limited or no infiltration, they are typically designed to provide enough hydraulic head to move flows through the underdrain connection to the storm drain system.

Treatment is achieved through filtration, sedimentation, sorption, biochemical processes and plant uptake.

Typical biofiltration components include:
• Inflow distribution mechanisms (e.g,perimeter flow spreader or filter strips) • Energy dissipation mechanism for concentrated inflows (e.g., splash blocks or riprap) • Shallow surface ponding for captured flows
• Side slope and basin bottom vegetation selected based on expected climate and ponding depth • Non-floating mulch layer
• Media layer (planting mix or engineered media) capable of supporting vegetation growth • Filter course layer consisting of aggregate to prevent the migration of fines into uncompacted native soils or the aggregate storage layer
• Aggregate storage layer with underdrain(s)
• Impermeable liner or uncompacted native soils at the bottom of the facility • Overflow structure
www.sandiegocounty.gov/stormwater E-115 Effective September 15, 2020

BF-1 Biofiltration
CURB W
W APRON FOR ENERGY MAINTENANCE.

DISSIPATION ACCESS
W W (AS NEEDED)
' W
A � CLEANOUT A'
CURB CUT.
12"MIN.

W w W W 29/( MAX.FINISH GRADE W3H:1V(MIN.) w 3H:1V(MIN.) UNDERDRAIN W
WyW yWW W OVERFLOW yW W WyWy
, . Wy � yW � y / E
y yWW � yWy
VEGETATED SIDE SLOPE MEDIA SURFACE AREA
PLAN

NOT TO SCALE
4-6"DROP FROM CURB CUT TO APRON
APRON FOR ENERGY DISSIPATION 2"MIN.FREEBOARD
3"SHREDDED HARDWOOD
6"MIN.TO 12"MAX. MULCH
SURFACE PONDING MAINTENANCE
CURBCUT CLEANOUT ACCESS
(AS NEEDED)
EXCAVATED SLOPE - OVERFLOW
(SHOWN AT 1H:1V) - STRUCTURE
MIN.18"MEDIA WITH
MIN.51N/HR _

FILTRATION RATE

IMPERMEABLE LINER

SATURATED STORAGE
(OPTIONAL) MIN.3"AGGREGATE BELOW UNDERDRAIN
FILTER COURSE MIN.6"DIAMETER UNDERDRAIN

AGGREGATE STORAGE LAYER

EXISTING UNCOMPACTED SOILS

SECTION A-A'

NOT TO SCALE
Typical plan and Section view of a Biofiltration BMP
Design Adaptations for Project Goals
Biofiltration Treatment BMP for storm water pollutant control. The system is lined or un-lined to provide incidental infiltration, and an underdrain is provided at the bottom to carry away filtered runoff.This configuration is considered to provide biofiltration treatment via flow through the media www.sandiegocounty.gov/stormwater E-116 Effective September 15, 2020

BF-1 Biofiltration
layer. Storage provided above the underdrain within surface ponding,media, and aggregate storage is considered included in the biofiltration treatment volume. Saturated storage within the aggregate storage layer can be added to this design by raising the underdrain above the bottom of the aggregate storage layer or via an internal weir structure designed to maintain a specific water level elevation.

Integrated storm water flow control and pollutant control configuration. The system can be designed to provide flow rate and duration control by primarily providing increased surface ponding and/or having a deeper aggregate storage layer above the underdrain. This will allow for significant detention storage,which can be controlled via inclusion of an outlet structure at the downstream end of the underdrain.

Recommended Siting Criteria _
Siting Criteria Intent/Rationale
Placement observes geotechnical
recommendations regarding potential hazards
� (e.g., slope stability,landslides,liquefaction Must not negatively impact existing site zones) and setbacks (e.g., slopes, foundations, geotechnical concerns. utilities).

Lining prevents storm water from
An impermeable liner or other hydraulic impacting groundwater and/or sensitive restriction layer is included if site constraints environmental or geotechnical features. ❑ indicate that infiltration or lateral flows should Incidental infiltration,when allowable, not be allowed. can aid in pollutant removal and groundwater recharge.

The thickness of the Impermeable Liner shall Considerations when choosing an be 30 MIL per County Green Streets Design Impermeable Liner may include ❑ Standard Drawing GS-3.00 and County Green placement methods, media and Streets Supplement to Caltrans Specifications underlying soil characteristics, and 20-11.08B. intended design life among others.

Bigger BMPs require additional design
features for proper performance.

Contributing tributary area greater than 5
acres may be allowed at the discretion of
Contributing tributary area must be www.sandiegocounty.gov/stormwater E-117 Effective September 15, 2020

BF-1 Biofiltration
Siting Criteria Intent/Rationale
Finish grade of the facility is _ 6 and www.sandiegocounty.gov/stormwater E-118 Effective September 15, 2020

BF-1 Biofiltration
Siting and Design Intent/Rationale
Vegetation
Plantings are suitable for the climate and Plants suited to the climate and ❑ expected ponding depth.A plant list to aid in ponding depth are more likely to selection can be found in Appendix F. survive.

An irrigation system with a connection to Seasonal irrigation might be needed to ❑ water supply should be provided as needed. keep plants healthy.

Mulch (Mandatory)
3 inches of well-aged, shredded hardwood Mulch will suppress weeds and ❑ mulch. maintain moisture for plant growth.

Media Layer
A filtration rate of at least 5 inches per
Media maintains a minimum filtration rate hour allows soil to drain between events. The initial rate should be higher
of 5 in/hr over lifetime of facility. An initial than long term target rate to account filtration rate of 8 to 12 in/hr is
❑ recommended to allow for clogging over for clogging over time. However an time; the initial filtration rate should not excessively high initial rate can have a negative impact on treatment
exceed 12 inches per hour.
performance, therefore an upper limit
is needed.

Media is a minimum 18 inches deep,
A deep media layer provides additional
meeting either of these two media
specifications: Appendix F.2 Biofiltration filtration and supports plants with Soil Media (BSM) or County of San Diego deeper roots.

Low Impact Development Handbook:

Appendix G -Bioretention Soil Specification Standard specifications must be ❑ Qune 2014, unless superseded by more followed. recent edition).

Alternatively, for proprietary designs and
custom media mixes not meeting the media For non-standard or proprietary specifications, the media meets the pollutant designs, compliance with F.1.1 ensures treatment performance criteria in Section that adequate treatment performance F.1.1. will be provided.
www.sandiegocounty.gov/stormwater E-119 Effective September 15, 2020

BF-1 Biofiltration
Siting and Design Intent/Rationale
Greater surface area to tributary area
ratios: a) maximizes volume retention
as required by the MS4 Permit and b)
decrease loading rates per square foot
and therefore increase longevity.

Media surface area is 3% of contributing Adjusted runoff factor is to account for area times adjusted runoff factor or greater.

El Unless demonstrated that the BMP surface site design BMPs implemented area can be smaller than 3%. upstream of the BMP (such as rain barrels,impervious area dispersion,
etc.). Refer to Appendix B guidance.

If media surface area is under 3% of
contributing area,refer to Sediment
Loading calculations in Appendix B.

Potential for pollutant export is partly a
Where receiving waters are impaired or have function of media composition; media a TMDL for nutrients, the system is design must minimize potential for designed with nutrient sensitive media export of nutrients,particularly where design (see fact sheet BF-2). receiving waters are impaired for nutrients.

Filter Course Layer
A filter course is used to prevent migration Migration of media can cause clogging of fines through layers of the facility. Filter of the aggregate storage layer void fabric is not used. spaces or subgrade. Filter fabric is more likely to clog.

Filter course is a minimum of 6 inches thick
provided in two separate 3 inch layers. The To prevent reduction of the available top layer shall be made of ASTM C33 storage volume that would lead to ❑ choker sand and the bottom layer shall be of clogging of the underdrain and native ASTM No. 8 aggregate. Marker stakes shall soil beneath the BMP. be used to ensure uniform lift thickness.

Washing aggregate will help eliminate
❑ Filter course is washed and free of fines. fines that could clog the facility and impede infiltration.

Gradation relationship between layers
Filter course calculations assessing suitability can evaluate factors (e.g.,bridging, for particle migration prevention have been permeability, and uniformity) to completed. determine if particle sizing is
appropriate or if an intermediate layer
is needed.
www.sandiegocounty.gov/stormwater E-120 Effective September 15, 2020

BF-1 Biofiltration
Siting and Design Intent/Rationale
Aggregate Storage Layer
Class 2 Permeable per Caltrans specification
68-1.025 is recommended for the storage
layer. Washed, open-graded crushed rock Washing aggregate will help eliminate � may be used, however a 4-6 inch washed pea fines that could clog the aggregate gravel filter course layer at the top of the storage layer void spaces or subgrade. crushed rock is required.

The depth of aggregate provided (12-inch
typical) and storage layer configuration is Proper storage layer configuration and � adequate for providing conveyance for underdrain placement will minimize facility drawdown time.
underdrain flows to the outlet structure.

Inflow, Underdrain, and Outflow Structures
Inflow,underdrains and outflow structures Maintenance will prevent clogging and are accessible for inspection and ensure proper operation of the flow maintenance. control structures.

Inflow velocities are limited to 3 ft/s or less
or use energy dissipation methods. (e.g., High inflow velocities can cause riprap,level spreader) for concentrated erosion, scour and/or channeling. inflows.

Curb cut inlets are at least 12 inches wide, Inlets must not restrict flow and apron have a 4-6 inch reveal (drop) and an apron prevents blockage from vegetation as it and energy dissipation as needed. grows in. Energy dissipation prevents erosion.

A minimal separation from subgrade or
Underdrain outlet elevation should be a the liner lessens the risk of fines entering the underdrain and can
minimum of 3 inches above the bottom
improve hydraulic performance by
elevation of the aggregate storage layer.
allowing perforations to remain
unblocked.

F1 Minimum underdrain diameter is 6 inches. Smaller diameter underdrains are prone to clogging.

Inflow, Underdrain, and Outflow Structures
Underdrains are made of slotted,PVC pipe Slotted underdrains provide greater conforming to ASTM D 3034 or equivalent intake capacity, clog resistant drainage, ❑ or corrugated,HDPE pipe conforming to and reduced entrance velocity into the AASHTO 252M or equivalent. pipe, thereby reducing the chances of solids migration.
www.sandiegocounty.gov/stormwater E-121 Effective September 15, 2020

BF-1 Biofiltration
Siting and Design Intent/Rationale
An underdrain cleanout with a minimum 6-
inch diameter and lockable cap is placed Properly spaced cleanouts will facilitate every 250 to 300 feet as required based on underdrain maintenance. underdrain length.

Overflow is safely conveyed to a
downstream storm drain system or discharge
point Size overflow structure to pass 100- Planning for overflow lessens the risk year peak flow for on-line infiltration basins of property damage due to flooding. and water quality peak flow for off-line
basins.

Conceptual Design and Sizing Approach for Storm Water Pollutant Control Only To design biofiltration for storm water pollutant control only(no flow control required),the following steps should be taken:

1. Verify that siting and design criteria have been met, including placement requirements, contributing tributary area, maximum side and finish grade slopes, and the recommended media surface area tributary ratio.

2. Calculate the DCV per Appendix B based on expected site design runoff for tributary areas.

3. Use the sizing worksheet presented in Appendix B.5 to size biofiltration BMPs.

Conceptual Design and Sizing Approach when Storm Water Flow Control is Applicable Control of flow rates and/or durations will typically require significant surface ponding and/or aggregate storage volumes, and therefore the following steps should be taken prior to determination of storm water pollutant control design. Pre-development and allowable post-project flow rates and durations should be determined as discussed in Chapter 6 of the manual.

1. Verify that siting and design criteria have been met, including placement requirements, contributing tributary area, maximum side and finish grade slopes, and the recommended media surface area tributary ratio.

2. Iteratively determine the facility footprint area,surface ponding and/or aggregate storage layer depth required to provide detention storage to reduce flow rates and durations to allowable limits. Flow rates and durations can be controlled from detention storage by altering outlet structure orifice size(s) and/or water control levels. Multi-level orifices can be used within an outlet structure to control the full range of flows.

3. If bioretention with underdrain cannot fully provide the flow rate and duration control required by this manual,an upstream or downstream structure with significant storage volume such as an underground vault can be used to provide remaining controls. www.sandiegocounty.gov/stormwater E-122 Effective September 15, 2020

BF-1 Biofiltration

4. After bioretention with underdrain has been designed to meet flow control requirements, calculations must be completed to verify if storm water pollutant control requirements to treat the DCV have been met.

Maintenance Overview
Normal Expected Maintenance. Biofiltration requires routine maintenance to: remove accumulated materials such as sediment, trash or debris; maintain vegetation health; maintain infiltration capacity of the media layer; replenish mulch; and maintain integrity of side slopes, inlets, energy dissipators,and outlets.A summary table of standard inspection and maintenance indicators is provided within this Fact Sheet.

Non-Standard Maintenance or BMP Failure. If any of the following scenarios are observed, the BMP is not performing as intended to protect downstream waterways from pollution and/or erosion.

Corrective maintenance,increased inspection and maintenance,BMP replacement,or a different BMP type will be required.
• The BMP is not drained between storm events. Surface ponding longer than approximately 24 hours following a storm event may be detrimental to vegetation health,and surface ponding longer than approximately 96 hours following a storm event poses a risk of vector (mosquito) breeding. Poor drainage can result from clogging of the media layer, filter course, aggregate storage layer, underdrain, or outlet structure. The specific cause of the drainage issue must be determined and corrected.
• Sediment, trash, or debris accumulation greater than 25% of the surface ponding volume within one month. This means the load from the tributary drainage area is too high,reducing BMP function or clogging the BMP. This would require pretreatment measures within the tributary area draining to the BMP to intercept the materials. Pretreatment components, especially for sediment,will extend the life of components that are more expensive to replace such as media, filter course, and aggregate layers.
• Erosion due to concentrated storm water runoff flow that is not readily corrected by adding erosion control blankets, adding stone at flow entry points, or minor re-grading to restore proper drainage according to the original plan. If the issue is not corrected by restoring the BMP to the original plan and grade, the County reviewer shall be contacted prior to any additional repairs or reconstruction.

Other Special Considerations. Biofiltration is a vegetated structural BMP. Vegetated structural BMPs that are constructed in the vicinity of, or connected to, an existing jurisdictional water or wetland could inadvertently result in creation of expanded waters or wetlands. As such, vegetated structural BMPs have the potential to come under the jurisdiction of the United States Army Corps of Engineers, SDRWQCB, California Department of Fish and Wildlife,or the United States Fish and Wildlife Service. This could result in the need for specific resource agency permits and costly mitigation to perform maintenance of the structural BMP.Along with proper placement of a structural www.sandiegocounty.gov/stormwater E-123 Effective September 15, 2020

BF-1 Biofiltration
BMP,routine maintenance is key to preventing this scenario.

Sediment Loading. Consider the effects of BMP design and tributary area land uses on the clogging potential of the BMP. Complete the sediment loading analysis included in Appendix F. www.sandiegocounty.gov/stormwater E-124 Effective September 15, 2020

BF-1 Biofiltration
Summary of Standard Inspection and Maintenance , The property owner is responsible to ensure inspection, operation and maintenance of permanent BMPs on their property unless responsibility has been formally transferred to an agency,community facilities district,homeowners association,property owners association, or other special district.

Maintenance frequencies listed in this table are average/typical frequencies.Actual maintenance needs are site-specific,and maintenance may be required more frequently. Maintenance must be performed whenever needed, based on maintenance indicators presented in this table.

The BMP owner is responsible for conducting regular inspections to see when maintenance is needed based on the maintenance indicators.

During the first year of operation of a structural BMP,inspection is recommended at least once prior to August 31 and then monthly from September through May.Inspection during a storm event is also recommended.After the initial period of frequent inspections,the minimum inspection and maintenance frequency can be determined based on the results of the first year inspections.

Threshold/Indicator Maintenance Action Inspection and Maintenance Frequency Accumulation of sediment,litter, or debris Remove and properly dispose of •Inspect monthly.If the BMP is 25%full*or accumulated materials, without damage to more in one month, increase inspection the vegetation or compaction of the media frequency to monthly plus after every 0.1- layer. inch or larger storm event.
•Remove any accumulated materials found
at each inspection.

Obstructed inlet or outlet structure Clear blockage. •Inspect monthly and after every 0.5-inch or larger storm event.
•Remove any accumulated materials found
at each inspection.

Damage to structural components such as Repair or replace as applicable •Inspect annually. weirs,inlet or outlet structures •Maintain when needed.

Poor vegetation establishment Re-seed, re-plant, or re-establish vegetation •Inspect monthly. per original plans. •Maintain when needed.
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BF-1 Biofiltration
• •/Indicator Maintenance Action • . Maintenance Frequency Dead or diseased vegetation Remove dead or diseased vegetation,re-seed, •Inspect monthly. re-plant, or re-establish vegetation per •Maintain when needed. original plans.

Overgrown vegetation Mow or trim as appropriate. •Inspect monthly. •Maintain when needed.
2/3 of mulch has decomposed, or mulch has Remove decomposed fraction and top off •Inspect monthly. been removed with fresh mulch to a total depth of 3 inches. •Replenish mulch annually, or more frequently when needed based on
inspection.

Erosion due to concentrated irrigation flow Repair/re-seed/re-plant eroded areas and •Inspect monthly. adjust the irrigation system. •Maintain when needed.

Erosion due to concentrated storm water Repair/re-seed/re-plant eroded areas, and •Inspect after every 0.5-inch or larger storm runoff flow make appropriate corrective measures such event. If erosion due to storm water flow as adding erosion control blankets, adding has been observed, increase inspection stone at flow entry points, or minor re- frequency to after every 0.1-inch or larger grading to restore proper drainage according storm event. to the original plan. If the issue is not •Maintain when needed. If the issue is not corrected by restoring the BMP to the corrected by restoring the BMP to the original plan and grade, the County reviewer original plan and grade, the County shall be contacted prior to any additional reviewer shall be contacted prior to any repairs or reconstruction. additional repairs or reconstruction.

Standing water in BMP for longer than 24 Make appropriate corrective measures such •Inspect monthly and after every 0.5-inch or hours following a storm event as adjusting irrigation system, removing larger storm event. If standing water is obstructions of debris or invasive vegetation, observed increase inspection frequency to Surface ponding longer than approximately � p q y 24 hours following a storm event may be clearing underdrains, or repairing/replacing after every 0.1-inch or larger storm event. detrimental to vegetation health clogged or compacted soils. •Maintain when needed. www.sandiegocounty.gov/stormwater E-126 Effective September 15, 2020

BF-1 Biofiltration
• •/Indicator Maintenance Action • . Maintenance Frequency Presence of mosquitos/larvae If mosquitos/larvae are observed: first, •Inspect monthly and after every 0.5-inch or immediately remove any standing water by larger storm event. If mosquitos are For images of egg rafts,larva,pupa,and adult dispersing to nearby landscaping; second, observed, increase inspection frequency to mosquitos, see make corrective measures as applicable to after every 0.1-inch or larger storm event. http://www.mosquito.org/biology restore BMP drainage to prevent standing •Maintain when needed. water.

If mosquitos persist following corrective
measures to remove standing water, or if the
BMP design does not meet the 96-hour
drawdown criteria due to release rates
controlled by an orifice installed on the
underdrain, the County reviewer shall be
contacted to determine a solution. A
different BMP type,or a Vector Management
Plan prepared with concurrence from the
County of San Diego Department of
Environmental Health,may be required.

Underdrain clogged Clear blockage. Inspect if standing water is observed for longer than 24-96 hours following a storm
event.

Maintain when needed.
"25%full"is defined as '/a of the depth from the design bottom elevation to the crest of the outflow structure (e.g.,if the height to the outflow opening is 12 inches from the bottom elevation,then the materials must be removed when there is 3 inches of accumulation—this should be marked on the outflow structure). www.sandiegocounty.gov/stormwater E-127 Effective September 15, 2020

SD-A Tree Wells
E.2 SD-A Tree Wells
MS4 Permit Category
r _ Site Design
Retention
Manual Category
Site Design
*�•t ',, Infiltration
Applicable Performance
Standard
Site Design
Pollutant Control
_ Flow Control
Primary Benefits
Volume Reduction
ree ells ource County of an ie o anual—E A nc.

Description ■
Trees planted to intercept rainfall and runoff as described in this fact sheet may be used as storm water management measures to provide runoff reduction of the DCV per Appendix B.1.4. Additional benefits associated with tree wells,include energy conservation,air quality improvement,and aesthetic enhancement. In addition to the requirements provided in this fact sheet, tree wells located in the County Right-of-Way shall follow requirements in Appendix K of this manual. Deviations from the outlined criteria may be approved at the discretion of County staff. Typical storm water management benefits associated with trees include:
• Interception of rainfall — tree surfaces (roots, foliage, bark, and branches) intercept, evaporate, store, or convey precipitation to the soil before it reaches surrounding impervious surfaces
• Reduced erosion—trees protect denuded area by intercepting or reducing the velocity of rain drops as they fall through the tree canopy
• Increased infiltration—soil conditions created by roots and fallen leaves promote infiltration • Treatment of storm water—trees provide treatment through uptake of nutrients and other storm water pollutants (phytoremediation) and support of other biological processes that break down pollutants
www.sandiegocounty.gov/stormwater E-4 Effective September 15,2020

SD-A Tree Wells
Typical tree well system components
include:
• Trees of the appropriate
species for site conditions and
constraints. Refer to the Plant
List in this fact sheet. OPTIONAL
GRATE
• Available soil media reservoir CURB' CURBCUT RUNOFF / INLET SIDEWALKSECTIDN
volume based on mature tree
PAVEMENT SURFACE PONDING REA DISTRIBUTION LAYER size, soil type, water SECTION
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
availability, surrounding land W W W % W W W W ° `W W W W W W W W Wu 0 0°O°�°0 0°O °O°O O°O °O°O 0 °O° uses, and project goals W W W V W W W W W W o°p°0 °O°o Q o°O o°O°o°0 °o° ° ° ° °
W W v W W W W W O O°O°O° °O °O°O O°O°
• Optional suspended pavement W W W W W NATIVE SOIL o°o°o°o° TREE WELL SOIL o °o°o°o °o° design to provide structural W W W W ° ° ° 0 0°o°a°o 0 0 0 0 0°o 0 0 0°a °
W W v W W W W W W o °
W W W W W W W W W O D°O°O°O°O°O °O°D°O OPTIONAL°O O° support for adjacent pavement ° UNDERDRAIN
W W W W O°O°O°O°O°O°O °O°O° O.

W w W OPTIONAL-
without O OO o
requiring compaction W W BARRIER W W
of underlying layers
• Optional root barrier devices Schematic of Tree Well as needed; a root barrier is a
device installed in the ground,between a tree and the sidewalk,intended to guide roots down and away from the sidewalk in order to prevent sidewalk lifting from tree roots. • Optional tree grates; to be considered to maximize available space for pedestrian circulation and to protect tree roots from compaction related to pedestrian circulation; tree grates are typically made up of porous material that will allow the runoff to soak through. • Optional shallow surface depression for ponding of excess runoff • Optional planter box drain
Design Adaptations for Project Goals ' ■ Site design BMP to provide incidental treatment. Trce wells primarily function as site design BMPs for incidental treatment.

Pollutant Control BMP to provide treatment. Project proponents are allowed to design trees to reduce the volume of stormwater runoff that requires treatment, (the Design Capture Volume [DCV]), or completely fulfill the pollutant control BMP requirements by retaining the entire DCV. Benefits from tree wells are accounted for by using the volume reduction values in Table B.1-3 presented in Appendix B. This credit can apply to other trees that are used for landscaping purposes that meet the same criteria.Project proponents are required to provide calculations supporting the amount of credit claimed from implementing trees within the project footprint.

Flow Control BMP to meet hydromodification requirements.Project proponents are also allowed to design tree wells as a flow control BMP. Benefits from tree wells are accounted for by using the DCV multipliers listed below. Project proponents are required to provide calculations showing that the entire DCV including the DCV multiplier is retained. www.sandiegocounty.gov/stormwater E-5 Effective September 15,2020

SD-A Tree Wells
Design Criteria and Considerations
Tree Wells, whether designed as Site Design BMPs, as Stormwater Pollutant Control BMP, or as a Flow Control BMP must meet the following design criteria and considerations, and if placed in the right-of-way must be consistent with the County of San Diego Green Streets Design Criteria and Green Streets Standard Drawings in Appendix K.Deviations from the below criteria may be approved at the discretion of the County staff if it is determined to be appropriate:

Siting and Design Intent/Rationale
Tree species is appropriately chosen for the
development (private or public). For public
rights-of-ways,local planning guidelines and Proper tree placement and species zoning provisions for the permissible species selection minimizes problems such as El and placement of trees are consulted. A list of pavement damage by surface roots and trees appropriate for site design that can be poor growth. used by all county municipalities are provided
in this fact sheet.

Tree well placement: ensure area is graded; Minimizes short-circuiting of run off and and the well is located so that full amount of assures DCV reductions are retained DCV reduction drains to the well. onsite.

Location of trees planted along public
streets follows guidance on green
infrastructure (Appendix K).Vehicle and
pedestrian line of sight and clear recovery
zones are considered in tree selection and
placement.

Unless exemption is granted by County staff
the following minimum tree separation
distance is followed
Improvement Mimmurn distance Roadway safety for both vehicular and to tree well pedestrian traffic is a key consideration Traffic Signal,Stop sign 20 feet for placement along public streets.

Underground Utility lines 5 feet
(except sewer)
Sewer Lines 10 feet
Above ground utility
structures (Transformers, 10 feet
Hydrants,Utility poles,etc.)
Driveways 10 feet
Intersections(intersecting 25 feet
curb lines of two streets)
www.sandiegocounty.gov/stormwater E-6 Effective September 15,2020

SD-A Tree Wells
Siting and Design Intent/Rationale
Tree growth can damage utilities and
Underground utilities and overhead wires overhead wires resulting in service are considered in the design and avoided or interruptions. Protecting utilities routed circumvented. Underground utilities are routed through the planter prevents damage and ❑ around or through the planter in suspended service interruptions. Refer to Section pavement applications. All underground 6.6 of the Green Streets Design Criteria utilities are protected from water and root in Appendix K for guidelines regarding penetration. utility placement and potential conflict with BMP facilities.

Suspended pavement designs as shown
in Page 7 of the Green Streets
Suspended pavement was used for confined Guidelines in Appendix K provide Tree Well soil volume. Suspended pavement structural support without compaction design was developed where appropriate to of the underlying layers, thereby � minimize soil compaction and improve
promoting tree growth.
infiltration and filtration capabilities. Recommended structural cells include Suspended pavement was constructed with an poured in place concrete columns, Silva approved structural cell. Cells manufactured by Deeproot Green Infrastructures and Stratacell and
Stratavault systems manufactured by
Citygreen Systems.

A minimum soil volume of 2 cubic feet per
square foot of mature tree canopy projection
area is provided for each tree. Canopy
projection area is the ground area beneath the
mature tree,measured at the drip line. Soil The minimum soil volume ensures that volume must be within 1.5 times the mature there is adequate storage volume to allow tree canopy radius. Soil depth shall be a for unrestricted evapotranspiration and ❑ minimum of 30 inches deep,preferably 36 infiltration. inches deep. When placing tree well next to
curb use Structural Soil as outlined in the
section below titled "Confined Tree Well Soil
Volume" and use Specifications in Appendix
K Use Amended Soil per Fact Sheet SD-F in
all other cases.
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SD-A Tree Wells
Siting and Design Intent/Rationale
To claim credit for existing trees, the root
structure of existing tree shall be protected and
additional soil volumes provided to meet the
above requirements.

A berm or well must be constructed around The minimum soil volume ensures that the perimeter of the soil volume to be credited there is adequate storage volume to allow ❑ and an inlet structure must be of the for unrestricted storage, appropriate size to allow runoff to enter the evapotranspiration, and infiltration. well.

Considerations should be made to prevent
root and water intrusion damage to
surrounding infrastructure.

The minimum tributary area ensures that
the tree receives enough runoff to fully
DCV from the tributary area draining to the utilize the infiltration and tree is equal to or greater than the tree credit evapotranspiration potential provided. In volume cases where the minimum tributary area
is not provided, the tree credit volume
must be reduced proportionately to the
actual tributary area.

Design requirement to ensure that the
runoff from the tributary area does not
bypass the BMP.

Inlet opening to the tree that is at least 18
Different inlet openings and drops in
inches wide. grade may be allowed at the discretion of A minimum 2 inch drop in grade from the County staff if calculations are shown ❑ inlet to the finish grade of the tree. that the diversion flow rate (Appendix Grated inlets are allowed for pedestrian B.) from the tributary area can be circulation. Grates need to be ADA compliant conveyed to the tree. In cases where the and have sufficient slip resistance. inlet capacity is limiting the amount of runoff draining to the tree, the tree credit
volume must be reduced
proportionately.

Conceptual Design and Sizing Approach for Site Design
Determine the areas where tree wells can be used in the site design to achieve incidental treatment.

Tree wells reduce runoff volumes from the site. Refer to Appendix B.2. Document the proposed tree locations in the SWQMP.
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SD-A Tree Wells
Conceptual Design and Sizing Approach for Pollutant Control When trees are proposed as a storm water pollutant control BMP,the project proponent must submit detailed calculations for the DCV treated by trees.Document the proposed tree locations on the BMP Plan&DMA Map,and provide sizing calculations in the SWQMP Attachment following the steps in Appendix B.

Conceptual Design and Sizing Approach for Flow Control
When trees are proposed as a flow control BMP, the project proponent must submit detailed calculations for the Required Retention Volume (RRV) treated by trees. Document the proposed tree locations on the BMP Plan&DMA Map,and provide sizing calculations in the SWQMP Attachment.

Tree Wells that are designed to meet flow control requirements are designated as SSD BMPs.

1. Determine how much volume you need.The Required Retention Volume (RRV)is the volume of rainfall that must be retained by the tree wells in the DMA to meet flow control requirements.

It is calculated by multiplying the DCV by a DCV multiplier. a. Determine the DCV. See Appendix B.
b. Determine the DCV Multiplier.The DCV Multiplier is based on two factors: (1)The tree well soil depth and, (2) The Hydrologic Soil Group. Once you know both values, determine the DCV Multiplier using this table:
c. Calculate the Required Retention Volume (DCV x DCV Multiplier). Calculate the RRV by multiplying the DCV by the DCV Multiplier. This is the volume of runoff that must be offset by the Tree Well Credit Volume. Repeat this process for each DMA.

Minimum Hydrologic Soil Group
Tree Well Soil A S C D
Depth(inches) (Default)
30" 1.60 2.20 2.50 2.90 L
V
36" 1.80 2.47 2.83 3.17
42" 2.00 2.73 3.17 3.43
4811 1 2.20 1 3.00 1 3.50 1 3.70 DCV Multiplier Table
Tree Well Soil Depth is the vertical distance from the top to the bottom of the soil layer in the tree well. Hydrologic Soil Group describes the native soil surrounding the tree well. Soil type affects how well water can infiltrate into the area surrounding the tree well. Group A soils provide the most infiltration and Group D the least. If your soil type is unknown, you can assume Group D. But this will result in larger DCV Multipliers, and in turn increase the size or number of tree wells needed.

Alternative Proposals: You can also propose RRV values or use methods and assumptions different than those described here.Proposals must be based on SWMM modeling or other methods acceptable to the County.
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SD-A Tree Wells

2. Determine how much volume you have.The Tree Well Credit Volume is the volume of runoff retention in cubic feet per tree (ft3/tree) to be provided by each tree well (or group) in the DMA.

Together retain a volume that is equal to or greater than the RRV for the DMA.

The volume credited for each tree well is based on the mature canopy diameter of the tree species selected.Any species listed below can be used in a tree well so long as it meets all other applicable restrictions and requirements for the project area.Native and drought tolerant species are required where feasible.

Mature Credit
10 Botanical Name 44ir Common Name Mature Canopy Volume Height Diameter per Tre
1 Ceanothus 'Ray Hartman" California Mountain Lillac 30 1 10 40 2 Pittosporum Phillyraeoides Willow Pittosporum 25 15 100 3 Salix Lasiole sis Arroyo Willow 25
4 Arbutus Unedo Strawberry Tree 30
5 Prunus llicifolia Hollyleaf Cherry 30 20 180 6 Prunus L noii Catalina Cherry 40
7 Ceras Ocadentaks Western Redbud 25 25 290 8 HeteromelesArbuti olia To on,Christmas Berry 25 9 Alnus Rhombifolia White Elder 75
10 Arbutus Marina' Hybrid Strawberry Tree 35
11 Chilopsis Linearis Desert Willow 30
12 Lyonothamnus Floribundus Catalina Ironwood 50 13 Magnolia Grandiora Southern Magnolia 40
14 Pinus Torreyana Torrey Pines 80 30 420 15 Platanus Racemosa California sycamore 60 16 Quercus Agrifolia Coast Live Oak 70
17 Quercus Engelmannii Engelmann Oak 50
18 Quercus Suber Cork Oak 40
19 Sambucus Mexicana Blue Elderberry 30
Tree Palette Table
Below are sources for Tree Palette Mature Height and Mature Canopy Diameter:

A. Water Efficient Landscape Design Manual, County of San Diego, 2016 B. Sustainable Landscapes Guidelines, San Diego County Water Authority,2015 C. Low Impact Development Handbook, County of San Diego,2014 D. Low Impact Development Design Manual, City of San Diego, 2011 E. Street Tree Selection Guide, City of San Diego, 2013 F. Environmentally Friendly Garden Plant List, City of San Diego, 2004 G. BMP Design Manual, County of San Diego, 2016
H. California Native Plant Society. 2017
Alternative Species. Tree species other than those listed are allowable,but must be approved by the County. If you know the mature canopy diameter of the species you want to propose,use the values in the table to determine its credit volume. Note that even if you select a species with a canopy diameter greater than 30 feet, the maximum credit any tree can generate is 420 ft3.

3. Determine if you have enough volume. Compare your total Tree Well Credit Volume from Step 2 to the RRV you calculated in Step 1. Once your Credit Volume is equal to or greater than www.sandiegocounty.gov/stormwater E-10 Effective September 15,2020

SD-A Tree Wells
your RRV, this requirement is satisfied. If your Credit Volume is initially too low, adjust your design either to (1) increase it with more or bigger trees, or (2) decrease the RRV through DCV reductions.

Tree wells will normally be placed at the discharge point of the DMA,either individually or in groups.

If some of them will retain runoff from different areas in the DMA,RRV and DCV calculations must be specific to each subarea.

If an underdrain is proposed for the Tree Well,the sizing factors shown in the DCV Multiplier Table cannot be used, and instead continuous simulation modeling should be performed. This would allow to obtain credit for soil volume underneath the underdrain.

Tree Planting Design in New or Reconstructed Streetscapes

1. Maximized open soil area for tree planting is the most cost effective method of achieving the required soil volume.

2. Tree wells within sidewalks shall have a minimum open area of four feet wide by six feet long.

Larger areas may be required to accommodate large root balls.

3. Tree well soil characteristics shall meet the requirements of SD-F Amended Soil.

Structural Requirements for Confined Tree Well Soil Volume In order to provide adequate soil volume for tree wells, soils may be placed confined beneath adjacent paved surfaces. Acceptable soil systems capable of carrying D-50 loading include structural soils, structural slabs, and structural cells:

1. Structural soil systems include CU-StructuralSod', Stalite Structural Soil, or equivalent.

2. Suspended pavements that allow uncompacted growing soil beneath the sidewalk include; structural slabs that span between structural supports, structural cells, and other commercially available structural systems. See Page 7 of the Green Streets Guidelines in Appendix K for illustrations. Manufacturer details and certification must be provided for commercial systems.

Structural calculations and details must be provided for structural slab installations. Structural cells are commercially-available structural systems placed subsurface that support the sidewalk and are filled with amended soil (SD-F). Manufacturer details and certification must be provided for commercial systems.

Stormwater Retention and Treatment Volume
Tree wells with expanded soil volume will serve as a method of capturing and retaining the required volume of stormwater in accordance with County requirements in Appendix B of this manual. These facilities can be designed to meet the County requirements when surface ponding volume is provided, whether designed as an enclosed plant bed with covered soil volume,or a continuous open area(either mulched or with turf) with soil volume under the adjacent sidewalk.

Maintenance Overview ==No W
Normal Expected Maintenance. Tree health shall be maintained as part of normal landscape maintenance. Additionally, ensure that storm water runoff can be conveyed into the tree well as www.sandiegocounty.gov/stormwater E-11 Effective September 15,2020

SD-A Tree Wells
designed. That is, the opening that allows storm water runoff to flow into the tree well (e.g., a curb opening,tree grate,or surface depression) shall not be blocked,filled,re-graded,or otherwise changed in a manner that prevents storm water from draining into the tree well. A summary table of standard inspection and maintenance indicators is provided within this Fact Sheet.

Non-Standard Maintenance or BMP Failure. Trees wells are site design BMPs that normally do not require maintenance actions beyond routine landscape maintenance. The normal expected maintenance described above ensures the BMP functionality. If changes have been made to the tree well entrance / opening such that runoff is prevented from draining into the tree well (e.g., a curb inlet opening is blocked by debris or a grate is clogged causing runoff to flow around instead of into the tree well,or a surface depression has been filled so runoff flows away from the tree well),the BMP is not performing as intended to protect downstream waterways from pollution and/or erosion.

Corrective maintenance will be required to restore drainage into the tree well as designed.

Surface ponding of runoff directed into tree wells is expected to infiltrate/evapotranspirate within 24- 96 hours following a storm event. Surface ponding longer than approximately 24 hours following a storm event may be detrimental to vegetation health, and surface ponding longer than approximately 96 hours following a storm event poses a risk of vector (mosquito) breeding. Poor drainage can result from clogging or compaction of the soils surrounding the tree. Loosen or replace the soils to restore drainage.

Other Special Considerations. Site design BMPs, such as tree wells, installed within a new development or redevelopment project are components of an overall storm water management strategy for the project. The presence of site design BMPs within a project is usually a factor in the determination of the amount of runoff to be managed with structural BMPs (i.e.,the amount of runoff expected to reach downstream retention or biofiltration basins that process storm water runoff from the project as a whole). When site design BMPs are not maintained or are removed, this can lead to clogging or failure of downstream structural BMPs due to greater delivery of runoff and pollutants than intended for the structural BMP. Therefore, the County Engineer may require confirmation of maintenance of site design BMPs as part of their structural BMP maintenance documentation requirements. Site design BMPs that have been installed as part of the project should not be removed, nor should they be bypassed by re-routing roof drains or re-grading surfaces within the project. If changes are necessary, consult the County Engineer to determine requirements. www.sandiegocounty.gov/stormwater E-12 Effective September 15,2020

SD-A Tree Wells
Summary of Standard Inspection and Maintenance .

The property owner is responsible to ensure inspection, operation and maintenance of permanent BMPs on their property unless responsibility has been formally transferred to an agency,community facilities district,homeowners association,property owners association, or other special district.

Maintenance frequencies listed in this table are average/typical frequencies.Actual maintenance needs are site-specific,and maintenance may be required more frequently. Maintenance must be performed whenever needed, based on maintenance indicators presented in this table.

The BMP owner is responsible for conducting regular inspections to see when maintenance is needed based on the maintenance indicators.

During the first year of operation of a structural BMP,inspection is recommended at least once prior to August 31 and then monthly from September through May.Inspection during a storm event is also recommended.After the initial period of frequent inspections,the minimum inspection and maintenance frequency can be determined based on the results of the first year inspections.

Threshold/
Tree health Routine actions as necessary to maintain tree •Inspect monthly. health. •Maintain when needed.

Dead or diseased tree Remove dead or diseased tree. Replace per •Inspect monthly. original plans. •Maintain when needed.

Standing water in tree well for longer than 24 Loosen or replace soils surrounding the tree •Inspect monthly and after every 0.5-inch hours following a storm event to restore drainage. or larger storm event. If standing water is Surface ponding longer than approximately observed,increase inspection frequency to 24 hours following a storm event may be after every 0.1-inch or larger storm event. detrimental to tree health •Maintain when needed.

Presence of mosquitos/larvae Disperse any standing water from the tree •Inspect monthly and after every 0.5-inch well to nearby landscaping. Loosen or or larger storm event. If mosquitos are For images of egg rafts,larva,pupa,and adult replace soils surrounding the tree to restore observed,increase inspection frequency to mosquitos, see drainage (and prevent standing water). after every 0.1-inch or larger storm event. htW:// www.mosquito.org/biolQgy •Maintain when needed www.sandiegocounty.gov/stormwater E-13 Effective September 15, 2020

SD-A Tree Wells
Threshold/ • • Inspection
Entrance / opening to the tree well is Make repairs as appropriate to restore •Inspect monthly. blocked such that storm water will not drain drainage into the tree well. •Maintain when needed. into the tree well (e.g., a curb inlet opening is
blocked by debris or a grate is clogged
causing runoff to flow around instead of into
the tree well; or a surface depression is filled
such that runoff drains away from the tree
well)
www.sandiegocounty.gov/stormwater E-14 Effective September 15, 2020

Appendix D — Employee Training Program
12 1205 Melrose Way
March 2021

TRAINED PERSONNEL LOG
Name of Person Date of Title of Training Location of Training Signature of Attending Training Person Attending
Training Training

Appendix E — Inspection Program
13 1205 Melrose Way
March 2021

BMP INSPECTION LOG
Name of Date of BMP Maintenance Performed Signature of Person/Company Maintenance Maintained Person Providing Providing Maintenance
Maintenance
Efficient
Irrigation and
Landscaping
Storm Drain
Inlet
Stenciling and
Signage
Biofiltration
Basin
Street
Sweeping

Appendix F — Maintenance Program
14 1205 Melrose Way
March 2021

BMP MAINTENANCE LOG
Name of Date of BMP Maintenance Performed Signature of Person/Company Maintenance Maintained Person Providing Providing Maintenance
Maintenance
Efficient
Irrigation and
Landscaping
Storm Drain
Inlet
Stenciling and
Signage
Biofiltration
Basin
Street
Sweeping

Appendix G — Cost Estimate
15 1205 Melrose Way
March 2021

COST ESTIMATE
BMP Quantity Inspection Annual O&M Start Up O&M Frequency Cost Cost Date (weekly/monthly/
quarterly)
Efficient Irrigation 1 $100 $400 Prior to Quarterly and Landscaping Occupancy
Storm Drain Inlet
Prior to
Stenciling and 3 $150 $500 Occupancy Quarterly Signage
Biofiltration Basin 1 Prior to
$125 $400 Occupancy Bi-annually
After rain event or
after visual
Street Sweeping 1 $100 $400 Prior to
Occupancy inspection shows
sediment
accumulation
Tree Wells 2 $20 $160 Prior to Monthly Occupancy
Total Annual / 10-year O&M Cost = $1,860/$18,600

1205 Melrose Way
ATTACHMENT 3B - MAINTENANCE AGREEMENT
All projects are required to maintain designed functionality of structural BMPs in perpetuity. Privately- owned projects must record a Storm Drain Maintenance Agreement with the County of San Diego Assessor's Office. A template Storm Drain Maintenance Agreement is available at:
http://www.cityofvista.com/services/city-departments/community-development/building-planning- permits-applications/land-development-autocad-templates/storm-water-forms

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