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HomeMy WebLinkAbout20190722_WQMP Report_07-16-2019Water Quality Management Plan
(WQMP)
CAMPBELL RESIDENCE
Lot 2, Tract No. 907
APN 423-247-02
605 Via Lido Soud, Newport Beach, California
Prepared for:
MS. BRIDGET CAMPBELL
605 Via Lido Soud
Newport Beach, CA 92663
Contact: Rosie Ou (949) 720-7022
Prepared by:
TOAL ENGINEERING, INC.
139 Avenida Navarro, San Clemente, CA 92672
www.toalengineering.com
Contact: ADAM L. TOAL, R.C.E. 59275 (949) 492-8586
atoal@toalengineering.com
Prepared on: JULY 16, 2019
Template Prepared: December 20, 2013
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Owner’s Certification
Project Owner’s Certification
Permit/Application No. ____-2019 Grading Permit No. ____-2019
Tract/Parcel Map No. Lot 2
Tract No. 907 Building Permit No. (TBD)
CUP, SUP, and/or APN (Specify Lot Numbers if Portions of Tract) 423-247-02
This Water Quality Management Plan (WQMP) has been prepared for Ms. Bridget Campbell by
Toal Engineering, Inc. The WQMP is intended to comply with the requirements of the local
NPDES Stormwater Program requiring the preparation of the plan.
The undersigned, while it owns the subject property, is responsible for the implementation of
the provisions of this plan and will ensure that this plan is amended as appropriate to reflect
up-to-date conditions on the site consistent with the current Orange County Drainage Area
Management Plan (DAMP) and the intent of the non-point source NPDES Permit for Waste
Discharge Requirements for the County of Orange, Orange County Flood Control District and
the incorporated Cities of Orange County within the San Diego Region (South Orange County)..
Once the undersigned transfers its interest in the property, its successors-in-interest shall bear
the aforementioned responsibility to implement and amend the WQMP. An appropriate
number of approved and signed copies of this document shall be available on the subject site in
perpetuity.
Owner:
Title Bridget Campbell
Company n/a
Address 605 Via Lido Soud, Newport Beach, CA 92663
Email
Telephone # (949) 720-7022
Signature Date
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Table of Contents
Contents Page No.
Section I Discretionary Permit(s) and Water Quality Conditions ..................................... 3
Section II Project Description .......................................................................................... 4
Section III Site Description ............................................................................................. 7
Section IV Best Management Practices (BMPs) ............................................................. 10
Section V Inspection/Maintenance Responsibility for BMPs .......................................... 28
Section VI Site Plan and Drainage Plan ......................................................................... 30
Section VII Educational Materials .................................................................................. 33
Attachments
Attachment A . .........................................................................................BMP Fact Sheets
Attachment B . ................................................................................. Educational Materials
Attachment C . .................................................................. Operation & Maintenance Plan
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section I
Page 3
Section I Discretionary Permit(s) and
Water Quality Conditions
Project Infomation
Permit/Application No. ____-2019 Tract/Parcel Map No. Lot 2
Tract No. 907
Additional Information/
Comments:
Water Quality Conditions
Water Quality
Conditions
(list verbatim)
None.
Watershed-Based Plan Conditions
Provide applicable
conditions from watershed
- based plans including
TMDLS.
TMDLs for Lower Newport Bay:
Nutrients (1998)
Toxics (2002)
Fecal Coliform (1999)
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section II
Page 4
Section II Project Description
II.1 Project Description
Description of Proposed Project
Development
Category
(Verbatim from
WQMP):
5. Impervious surface of 2,500 square feet or more located within, directly
adjacent to (within 200 feet), or discharging directly into receiving waters
within Environmentally Sensitive Areas (ESAs).
Project Area (ft2): 3,384 Number of Dwelling Units: 1 SIC Code: n/a
Narrative
Project
Description:
The project consists of the following: (1) demolition of the existing residence and
associated hardscape, from Via Lido Soud up to, but not including, the existing cmu
bulkhead wall adjacent to the bay and dock access; (2) construction of a new custom
single-family residence and appurtenant hardscape, landscape, and drainage
improvements.
Project Area Pervious Impervious
Area (sf) Percentage Area (sf) Percentage
Pre-Project Conditions 270 8 3,114 92
Post-Project Conditions 465 14 2,919 86
Drainage Patterns/Connections See Section III.2.
II.2 Potential Stormwater Pollutants
The following table lists the expected stormwater pollutants based on land uses and site activities
per Table 2.1 of the Technical Guidance Document for the Preparation of Conceptual/Preliminary
and/or Project Water Quality Management Plans (TGD).
Pollutants of Concern
Pollutant
Circle One:
E=Expected to
be of concern
N=Not Expected
to be of concern
Additional Information and Comments
Suspended-Solid / Sediment ◇E N
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section II
Page 5
Nutrients ◇E N
Heavy Metals E ◇N
Pathogens (Bacteria/Virus) ◇E N
Pesticides ◇E N
Oil and Grease ◇E N
Toxic Organic Compounds E ◇N
Trash and Debris ◇E N
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section II
Page 6
II.3 Hydrologic Conditions of Concern
Hydrologic Conditions of Concern (HCOCs) do not exist for this project since site runoff is
conveyed in a storm drain system and discharged directly into Newport Bay.
II.4 Post Development Drainage Characteristics
Post-construction surface drainage will be directed to the same ultimate discharge points as prior to
construction. Runoff from the site will be collected in an area drain system and discharged into an
infiltration trench at the front of the property. Storm flows that exceed the capacity of the trench
will discharge to the street. The drainage system is shown on the Precise Grading and Drainage
Plan and the Water Quality Management Plan for the project.
II.5 Property Ownership/Management
This property is privately owned by:
Ms. Bridget Campbell
605 Via Lido Soud
Newport Beach, CA 92663
Tel: (949) 720-7022
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section III
Page 7
Section III Site Description
III.1 Physical Setting
Planning Area/
Community Name N/A
Location/Address 605 Via Lido Soud, Newport Beach, California
Project Area Description
The subject property lies on the southerly side of Lido Isle inside
Newport Bay. The island is developed exclusively with single-
family residential units.
Land Use RSD-A: Single Unit Residential Detached (0.0-5.9 DU/AC)
Zoning R-1: Single Unit Residential
Acreage Property: 3,384 s.f. (0.078 acres)
Project: 3,384 s.f. (0.078 acres)
Predominant Soil Type Per the O.C. Hydrology Manual Plate B, the project is underlain by
soil Type A.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section III
Page 8
III.2 Site Characteristics
Precipitation Zone 0.7-in (TGD Fig XVI-1)
Topography The subject property is a relatively flat residential lot. Elevations on
the developed portion of the site range from a maximum of about 13.0-
feet to a minimum of about 12.0-feet. A bulkhead wall exists at the
back of the property separating the site from Newport Bay.
Drainage
Patterns/Connections
Under existing conditions, the runoff from the site flows Newport Bay
via the drain system in Via Lido Soud.
Soil Type, Geology, and
Infiltration Properties
Per the O.C. Hydrology Manual Plate B, the project is underlain by
soil Type A.
Hydrogeologic
(Groundwater) Conditions
The results of the exploratory drillings in the soils report, which has
been prepared by Coast Geotechnical, show that groundwater was
encountered at approximately 8.5-9.0’ below grade. The design
groundwater level is recommended to be at a level of 6 below grade,
or an elevation of approximately 6.0.
Geotechnical Conditions
(relevant to infiltration) According to infiltration BMP feasibility criteria, infiltration of the
entire DVC is feasible for this project.
Off-Site Drainage The project site does not receive run-on from adjacent properties.
Utility and Infrastructure
Information
Public and private utilities are already in place for this property.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section III
Page 9
III.3 Watershed Description
Receiving Waters Lower Newport Bay
303(d) Listed Impairments Chlordane, Copper, DDT, Indicator Bacteria, Nutrients, PCBs,
Pesticides, Sediment Toxicity
Applicable TMDLs Sediment, Nutrients, Toxics, Fecal Coliform
Pollutants of Concern for
the Project
Primary Pollutants of Concern:
Chlordane, Copper, DDT, Indicator Bacteria, Nutrients, PCBs, Pesticides,
Sediment Toxicity.
Other Pollutants of Concern:
None.
Environmentally Sensitive
and Special Biological
Significant Areas
Lower Newport Bay.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 10
Section IV Best Management Practices (BMPs)
IV. 1 Project Performance Criteria
Project Performance Criteria
If HCOC exists, list applicable
hydromodification control performance criteria
(MWQMP Appendix C)
Per Section II.3 of this report, HCOCs do not
exist for the proposed project.
List applicable
LID performance
criteria (Section
7.II-2.4.3 from
MWQMP)
• Priority Projects must infiltrate, harvest and use, evapotranspire, or
biotreat/biofilter, the 85th percentile, 24-hour storm event (Design
Capture Volume).
• A properly designed biotreatment system may only be considered if
infiltration, harvest and use, and evapotranspiration (ET) cannot be
feasibly implemented for the full design capture volume. In this case,
infiltration, harvest and use, and ET practices must be implemented to
the greatest extent feasible and biotreatment may be provided for the
remaining design capture volume.
Calculate LID
DCV for Project.
Simple Method per TGD III.1.1. 𝐷𝐷𝐷𝐷𝐷𝐷=𝐷𝐷 × 𝑑𝑑 × 𝐴𝐴 𝐷𝐷= (0.75 × 𝑖𝑖𝑚𝑚𝑚𝑚+ 0.15) = 0.75 × 0.86 + 0.15 = 0.80 𝑑𝑑= 0.70 𝑖𝑖𝑖𝑖. 𝐴𝐴= 3,384 𝑠𝑠𝑠𝑠.𝑓𝑓𝑓𝑓. 𝐷𝐷𝐷𝐷𝐷𝐷=0.80 x 0.70 𝑖𝑖𝑖𝑖.x 3,374 𝑠𝑠.𝑓𝑓.x �1 𝑓𝑓𝑓𝑓.12 𝑖𝑖𝑖𝑖.�=159 𝑐𝑐𝑓𝑓
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 11
Worksheet B: Simple Design Capture Volume Sizing Method
Step 1: Determine the design capture storm depth used for calculating volume
1 Enter design capture storm depth from Figure III.1, d (inches) d= 0.70 inches
2 Enter the effect of provided HSCs, dHSC (inches)
(Worksheet A) dHSC= 0.00 inches
3 Calculate the remainder of the design capture storm depth,
dremainder (inches) (Line 1 – Line 2) dremainder= 0.70 inches
Step 2: Calculate the DCV
1 Enter Project area tributary to BMP (s), A (acres) A= 0.078 acres
2 Enter Project Imperviousness, imp (unitless) imp= 0.86
3 Calculate runoff coefficient, C= (0.75 x imp) + 0.15 C= 0.80
4 Calculate runoff volume, Vdesign= (C x dremainder x A x 43560 x
(1/12)) Vdesign= 159 cu-ft
Step 3: Design BMPs to ensure full retention of the DCV
Step 3a: Determine design infiltration rate
1 Enter measured infiltration rate, Kmeasured (in/hr)
(Appendix VII) Kmeasured= In/hr
2 Enter combined safety factor from Worksheet H, Sfinal (unitless) Sfinal=
3 Calculate design infiltration rate, Kdesign = Kmeasured / Sfinal Kdesign= In/hr
Step 3b: Determine minimum BMP footprint
4 Enter drawdown time, T (max 48 hours) T= Hours
5 Calculate max retention depth that can be drawn down within the
drawdown time (feet), Dmax = Kdesign x T x (1/12) Dmax= feet
6 Calculate minimum area required for BMP (sq-ft), Amin = Vdesign/
dmax Amin= sq-ft
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 12
IV.2. SITE DESIGN AND DRAINAGE PLAN
Overview
The ultimate plan of development for the proposed project is shown on the WQMP Site Plan in
Section VI of this report. The project Precise Grading Plan shows the proposed grading, site
improvements, and retaining walls necessary for construction of a single-family residence.
Site Design Practices
The project incorporates Site Design practices as follows:
• Preserve Existing Drainage Patterns and Time of Concentration – The ultimate
points of discharge are the same for the pre- and post-project conditions. Time of
concentration will be similar, since pre-and post-project flow path lengths will be
similar.
Drainage Management Areas (DMAs)
The site has two Drainage Management Areas. Drainage from DMA-1 & DMA-2 is directed into a
shared infiltration trench at the front of the property. Storm flows exceeding the trench capacity will
be discharged to Via Lido Soud. All roof runoff will be pre-treated by a downspout filter (TRT-2)
prior to being discharged into the infiltration BMPs.
DMA-1 DMA-2
Total Area (ac) 0.041 0.036
Total Area (sf) 1,800 1,584
Impervious Area (sf) 1,431 1,488
Pervious Area (sf) 369 96
imp 0.80 0.94
C 0.75 0.86
d (in) 0.7 0.7
DCV (cf) 79 80
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 13
IV.3 BMP SELECTION AND PROJECT CONFORMANCE ANALYSIS
Each sub-section below documents that the proposed design features conform to the applicable
project performance criteria via check boxes, tables, calculations, narratives, and/or references to
worksheets.
IV.3.1 Hydrologic Source Controls
The Hydrologic Source Controls to be used for this project are indicated in the table below.
Implementation of said controls is discussed in the text that follows.
Name Included?
Localized on-lot infiltration
Impervious area dispersion (e.g. roof top disconnection)
Street trees (canopy interception)
Residential rain barrels (not actively managed)
Green roofs/Brown roofs
Blue roofs
Impervious area reduction (e.g. permeable pavers, site design)
Other:
Hydrologic Source Controls have not been used due to space constraints, including landscape area
size and proximity to structure foundations.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 14
IV.3.2 Infiltration BMPs
Infiltration BMPs to be used for this project are indicated in the table below. Implementation of said
controls is discussed in the text that follows.
Name Included?
Bioretention without underdrains
Rain gardens
Porous landscaping
Infiltration planters
Retention swales
Infiltration trenches
Infiltration basins
Drywells
Subsurface infiltration galleries
French drains
Permeable asphalt
Permeable concrete
Permeable concrete pavers
Other:
The sizing has been done per the City of Newport Beach’s prescriptive requirements of “One 15’
long French drain per maximum of 2,000 sf of impervious area”. The sizing for each DMA is:
DMA-1:
Area tributary to BMP = 1,800 s.f.
Gravel Volume within City’s 15’ Long Trench Drain = 15’L x 12”W x 12”D = 15 c.f.
Sizing for infiltration gravel = 1,800 s.f. x (15 c.f./2,000 s.f.) = 13.5 c.f. (min. volume) gravel area
DMA-2:
Area tributary to BMP = 1,584 s.f.
Gravel Volume within City’s 15’ Long Trench Drain = 15’L x 12”W x 12”D = 15 c.f.
Sizing for infiltration gravel = 1,584 s.f. x (15 c.f./2,000 s.f.) = 11.9 c.f. (min. volume) gravel area
SHARED INFILTRATION TRENCH FOR DMA-1 & DMA-2:
Provided Gravel Volume per Site Plan = 18” wide x 12” deep x 30’ long trench = 45 c.f.
13.5 c.f. + 11.9 c.f. = 25.4 c.f. < 45 c.f.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 15
Table 2.7: Infiltration BMP Feasibility Worksheet
Infeasibility Criteria Yes No
1
Would Infiltration BMPs pose significant risk for
groundwater related concerns? Refer to Appendix VII
(Worksheet I) for guidance on groundwater-related
infiltration feasibility criteria.
X
Provide basis:
Infiltration BMPs will not pose a significant risk to local groundwater. Groundwater in the vicinity of
the project site is not used for drinking water. Pretreatment devices will mitigate entry of trash,
sediment, and oil & grease into proposed infiltration BMPs.
2
Would Infiltration BMPs pose significant risk of
increasing risk of geotechnical hazards that cannot be
mitigated to an acceptable level? (Yes if the answer to
any of the following questions is yes, as established by a
geotechnical expert):
• The BMP can only be located less than 50 feet away
from slopes steeper than 15 percent
• The BMP can only be located less than eight feet from
building foundations or an alternative setback.
• A study prepared by a geotechnical professional or an
available watershed study substantiates that
stormwater infiltration would potentially result in
significantly increased risks of geotechnical hazards
that cannot be mitigated to an acceptable level.
X
Provide basis:
3 Would infiltration of the DCV from drainage area violate
downstream water rights? X
Provide basis:
There are no downstream water right holders since site drainage is conveyed via the city storm drain
system directly to receiving waters (Lower Newport Bay).
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 16
Table 2.7: Infiltration BMP Feasibility Worksheet (continued)
Partial Infeasibility Criteria Yes No
4
Is proposed infiltration facility located on HSG D soils or the
site geotechnical investigation identifies presence of soil
characteristics which support categorization as D soils?
X
Provide basis:
Proposed facility is located on HSG-A soils per OCHM Soil Maps.
5
Is measured infiltration rate below proposed facility
less than 0.3 inches per hour? This calculation shall be
based on the methods described in Appendix VII.
X
Provide basis:
Infiltration rate is presumed to be greater than 0.3 inches per hour based on site’s HSG.
6
Would reduction of over predeveloped conditions cause
impairments to downstream beneficial uses, such as
change of seasonality of ephemeral washes or
increased discharge of contaminated groundwater to
surface waters?
X
Provide citation to applicable study and summarize findings relative to the amount of infiltration
that is permissible:
No downstream beneficial uses such as ephemeral washes or groundwater sources of drinking
water are located downstream of the subject property.
7
Would an increase in infiltration over predeveloped
conditions cause impairments to downstream beneficial
uses, such as change of seasonality of ephemeral
washes or increased discharge of contaminated
groundwater to surface waters?
X
Provide citation to applicable study and summarize findings relative to the amount of infiltration
that is permissible:
No downstream beneficial uses such as ephemeral washes or groundwater sources of drinking
water are located downstream of the subject property.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 17
Table 2.7: Infiltration BMP Feasibility Worksheet (continued)
Infiltration Screening Results (check box corresponding to result):
8
Is there substantial evidence that infiltration from the
project would result in a significant increase in I&I to the
sanitary sewer that cannot be sufficiently mitigated? (See
Appendix XVII)
Provide narrative discussion and supporting evidence:
No evidence of I&I has been provided by the local sewer
agency (City of Newport Beach).
No
9
If any answer from row 1-3 is yes: infiltration of any volume
is not feasible within the DMA or equivalent.
Provide basis:
10
If any answer from row 4-8 is yes, infiltration is
permissible but is not presumed to be feasible for the
entire DCV. Criteria for designing biotreatment BMPs to
achieve the maximum feasible infiltration and ET shall
apply.
Provide basis:
11
If all answers to rows 1 through 10 are no, infiltration of the
full DCV is potentially feasible, BMPs must be designed to
infiltrate the full DCV to the maximum extent practicable.
X
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Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 18
IV.3.3 Evapotranspiration, Rainwater Harvesting BMPs
Evapotranspiration and/or Rainwater Harvesting BMPs to be used for this project are indicated in
the table below. Implementation of said controls is discussed in the text that follows.
Name Included?
All HSCs; See Section IV.3.1
Surface-based infiltration BMPs
Other vegetated BMPs
Above-ground cisterns and basins
Underground detention
Other:
The project site does not have an irrigation demand large enough to justify partial capture for
irrigation demand. See Worksheet J from Section X of the TGD on the following page.
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Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 19
Worksheet J: Summary of Harvested Water Demand and Feasibility
1 What demands for harvested water exist in the tributary area (check all that apply):
2 Toilet and urinal flushing □
3 Landscape irrigation □
4 Other:_______________________________________________________ □
5 What is the design capture storm depth? (Figure III.1) d .70 inches
6 What is the project size? A 0.078 ac
7 What is the acreage of impervious area? IA 0.078 ac
For projects with multiple types of demand (toilet flushing, irrigation demand, and/or other demand)
8 What is the minimum use required for partial capture? (Table
X.6) gpd
9 What is the project estimated wet season total daily use
(Section X.2)? gpd
10 Is partial capture potentially feasible? (Line 9 > Line 8?)
For projects with only toilet flushing demand
11 What is the minimum TUTIA for partial capture? (Table X.7)
12 What is the project estimated TUTIA?
13 Is partial capture potentially feasible? (Line 12 > Line 11?)
For projects with only irrigation demand
14 What is the minimum irrigation area required based on
conservation landscape design? (Table X.8) 0.84 x 0.078 = 0.065 ac
15 What is the proposed project irrigated area? (multiply
conservation landscaping by 1; multiply active turf by 2) 0.01 ac
16 Is partial capture potentially feasible? (Line 15 > Line 14?) No
Provide supporting assumptions and citations for controlling demand calculation:
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Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 20
IV.3.4 Biofiltration BMPs
Biofiltration BMPs to be used for this project are indicated in the table below. Implementation of said
controls is discussed in the text that follows.
Name Included?
Bioretention with underdrains
Stormwater planter boxes with underdrains
Proprietary vegetated biotreatment systems
Other:
The use of Biotreatment BMPs on the siteis not required because the entire site is being treated with
infitration trenches.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 21
IV.3.5 Hydromodification Control BMPs
Hydromodification controls are not required for this project because Hydrologic Conditions of
Concern do not exist for this project. See Section II.3.
Hydromodification Control BMPs
BMP Name BMP Description
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Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 22
IV.3.6 Non-structural Source Control BMPs
Non-structural source control BMPs used for this project are described below.
Non-Structural Source Control BMPs
Identifier Name
Check One If not applicable, state brief
reason Included Not
Applicable
N1 Education for Property Owners,
Tenants and Occupants
N2 Activity Restrictions
N3 Common Area Landscape
Management No common areas present.
N4 BMP Maintenance
N5 Title 22 CCR Compliance (How
development will comply) No hazardous waste.
N6 Local Industrial Permit Compliance Not an industrial project.
N7 Spill Contingency Plan No hazardous waste.
N8 Underground Storage Tank
Compliance No USTs on site.
N9 Hazardous Materials Disclosure
Compliance No hazardous waste.
N10 Uniform Fire Code Implementation No hazardous waste.
N11 Common Area Litter Control No common areas present.
N12 Employee Training No employees.
N13 Housekeeping of Loading Docks No loading docks exposed to
storm water proposed.
N14 Common Area Catch Basin Inspection No common areas present.
N15 Street Sweeping Private Streets and
Parking Lots No exterior parking areas.
N16 Retail Gasoline Outlets None exist.
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Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 23
N1 – Education: The Owner must understand purpose of all BMPs and how they work. The
contractor who installs the BMP shall educate the owner and the owner shall share the information
with any maintenance personnel. Additionally, the owner shall keep a copy of this WQMP, as well
as the Operations and Maintenance Plan. Practical information materials shall be provided to the
first residents /occupants/tenants on general housekeeping practices that contribute to the
protection of stormwater quality. These materials will be initially developed and provided to first
residents/occupants/tenants by the developer.
N2 – Activity Restrictions: The following actions are prohibited on the project site: (1) disposal of
solid waste on the property except in designated trash areas, (2) disposal of liquid waste into any
solid waste container, (3) placement of hazardous waste in any solid waste container. Any
activities that would violate the City of Newport Beach Water Quality Ordinance (Municipal Code
Chapter 14.36).
N4 – BMP Maintenance: The Owner shall be responsible for maintenance of BMPs as indicated in
Section V of this report.
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Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 24
IV.3.7 Structural Source Control BMPs
Structural source control BMPs used for this project are described below.
Structural Source Control BMPs
Identifier Name
Check One If not applicable, state brief
reason Included Not
Applicable
S1 Provide storm drain system stenciling
and signage Drain inlets on private property.
S2
Design and construct outdoor material
storage areas to reduce pollution
introduction
No outdoor MSAs.
S3
Design and construct trash and waste
storage areas to reduce pollution
introduction
S4
Use efficient irrigation systems &
landscape design, water conservation,
smart controllers, and source control
S5 Protect slopes and channels and
provide energy dissipation No proposed slopes or channels.
Incorporate requirements applicable to
individual priority project categories
(from SDRWQCB NPDES Permit)
S6 Dock areas None exist.
S7 Maintenance bays None exist.
S8 Vehicle wash areas None exist.
S9 Outdoor processing areas None exist.
S10 Equipment wash areas None exist.
S11 Fueling areas None exist.
S12 Hillside landscaping None exist.
S13 Wash water control for food
preparation areas None exist.
S14 Community car wash racks None exist.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 25
S3 – Trash Enclosures: The Owner shall keep trash storage areas clean and orderly to reduce
pollutant introduction. All trash container areas shall be paved with an impervious surface,
designed not to allow run-on, screened or walled to prevent off-site transport of trash, and be
provided with a roof or awning to prevent direct precipitation.
S4 – Efficient Irrigation: The proposed project will utilize efficient irrigation systems as specified
on the project landscape plans.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 26
IV.4 ALTERNATIVE COMPLIANCE PLAN (IF APPLICABLE)
IV.4.1 Request of Waiver of LID BMPs
Provide documentation of feasibility analysis if implementation of LID BMPs is technically
infeasible. Refer to Section 7.II-3.1 in the Model WQMP. Calculate the amount of remaining obligation
that must be met with alternative compliance (See TGD Appendix VI).
IV.4.2 Water Quality Credits
Determine if water quality credits are applicable for the project. Refer to Section 7.II-3.2 of the Model
WQMP for description of credits and TGD Appendix VI for calculation methods for applying WQ credits.
Description of Proposed Project
Project Types that Qualify for Water Quality Credits (Select all that apply):
Redevelopment
projects that reduce the
overall impervious
footprint of the project
site.
Brownfield redevelopment, meaning
redevelopment, expansion, or reuse of real
property which may be complicated by the
presence or potential presence of hazardous
substances, pollutants or contaminants, and
which have the potential to contribute to
adverse ground or surface WQ if not
redeveloped.
Higher density development projects which
include two distinct categories (credits can only
be taken for one category): those with more than
seven units per acre of development (lower credit
allowance); vertical density developments, for
example, those with a Floor to Area Ratio (FAR)
of 2 or those having more than 18 units per acre
(greater credit allowance).
Mixed use development, such as a
combination of residential, commercial,
industrial, office, institutional, or other land
uses which incorporate design principles
that can demonstrate environmental benefits
that would not be realized through single
use projects (e.g. reduced vehicle trip traffic
with the potential to reduce sources of water
or air pollution).
Transit-oriented developments, such as a mixed
use residential or commercial area designed to
maximize access to public transportation; similar to
above criterion, but where the development center is
within one half mile of a mass transit center (e.g. bus,
rail, light rail or commuter train station). Such
projects would not be able to take credit for both
categories, but may have greater credit assigned
Redevelopment
projects in an established
historic district, historic
preservation area, or
similar significant city
area including core City
Center areas (to be
defined through
mapping).
Developments with
dedication of undeveloped
portions to parks,
preservation areas and
other pervious uses.
Developments
in a city center
area.
Developments
in historic
districts or
historic
preservation
areas.
Live-work developments, a
variety of developments designed
to support residential and
vocational needs together –
similar to criteria to mixed use
development; would not be able
to take credit for both categories.
In-fill projects, the
conversion of empty lots
and other underused
spaces into more
beneficially used spaces,
such as residential or
commercial areas.
Calculation of
Water Quality
Credits (if
applicable)
This project does not qualify for the water quality credits listed above.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section IV
Page 27
IV.4.3 Treatment Control BMPs
Since the project is fully treated using Infiltration BMPs, utilization of Treatment Control BMPs is not
required. Additionally, due to the shallow nature of the groundwater, downspout filters are being
utilized as pre-treatment for the roof runoff prior to discharge into the infiltration trench.
Treatment Control BMPs
BMP Name BMP Description
IV.4.4 Regional/Sub-Regional LID BMPs
This project will not participate in Regional/Sub-Regional LID BMPs since the full DCV can be
treated using LID BMPs.
Regional/Sub-Regional LID BMPs
IV.4.5 Other Alternative Compliance Measures
This project will not make use of other alternative compliance measures since the full DCV can be
treated using LID BMPs.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MR. ANDREW GABRIEL Section V
Page 28
Section V Inspection/Maintenance
Responsibility for BMPs
Fill out information in table below. Prepare and attach an Operation and Maintenance Plan.
Identify the mechanism through which BMPs will be maintained. Inspection and maintenance
records must be kept for a minimum of five years for inspection by the regulatory agencies. Refer to
Section 7.II-4.0 in the Model WQMP.
BMP Inspection/Maintenance
BMP Reponsible
Party(s)
Inspection/
Maintenance
Activities Required
Minimum
Frequency of
Activities
INF-2
Infiltration
Trench
Owner or contracted maintenance personnel
Visual Inspection, keep free of debris, perform more thorough inspection after storm events. Media (Gravel) Replacement Filter Fabric Replacement
Twice yearly and immediately following each storm event. Every 10 years as req’d Once a year as req’d
TRT-2
Filter Insert
(Treatment)
Owner via
maintenance
contractors
• Filter Insert Replacement/Rotation
• Once a year. Refer to Manufacturer’s O&M plan on pages 36-39 for details.
• Remove Sediment and debris.
• Three times per year and after storm events. Refer to Manufacturer’s O&M plan on pages 36-39 for details.
N2 – Activity Restrictions Owner or contracted maintenance personnel Use dry cleanup methods.. Hazardous items shall be disposed of properly. As required.
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MR. ANDREW GABRIEL Section V
Page 29
N4 – BMP Maintenance Owner or contracted maintenance personnel
Visual Inspection, perform more thorough inspection if ponding water sits for more than 48 hours.
Twice yearly and immediately following each storm event.
S3 – Trash & Waste Storage Area
Owner or contracted maintenance personnel Keep trash storage areas clean and orderly. Weekly
S4 – Efficient Irrigation Owner or contracted maintenance personnel
Ensure that sprinklers are working properly and minimize unnecessary irrigation. Weekly
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section VI
Page 30
Section VI Site Plan and Drainage Plan
VI.1 SITE PLAN AND DRAINAGE PLAN
Include a site plan and drainage plan sheet set containing the following minimum information:
• Project location
• Site boundary
• Land uses and land covers, as applicable
• Suitability/feasibility constraints
• Structural BMP locations
• Drainage delineations and flow information
• Drainage connections
• BMP details
VI.2 ELECTRONIC DATA SUBMITTAL
The minimum requirement is to provide submittal of PDF exhibits in addition to hard copies.
Format must not require specialized software to open.
PA2019-142
WQMP LEGEND
PROPOSED BUILDING
PROPOSED LANDSCAPE
PROPOSED HARDSCAPE
RUNOFF FLOW DIRECTION
PROPOSED STORM DRAIN
INLET
PROJECT AREA BOUNDARY
INFILTRATION TRENCH / GRAVEL AREA
DETAIL
PERFORATED DRAIN TRENCH
ON-SITE PROJECT INFORMATION:
BMP TABLE
1 3 9 A v e n i d a N a v a r r o
San Clemente, CA 92672
9 4 9 . 4 9 2 . 8 5 8 6
www.toalengineering.com
CIVIL ENGINEERING
L A N D S U R V E Y I N G
STORMWATER QUALITY
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section VI
Page 31
Figure VI.1. Vicinity Map.
Source: maps.google.com
SITE
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section VI
Page 32
Figure VI.2. Aerial Image.
Source: maps.google.com
SITE
PA2019-142
Water Quality Management Plan (WQMP)
Campbell Residence – 605 Via Lido Soud, Newport Beach, California
MS. BRIDGET CAMPBELL Section VII
Page 33
Section VII Educational Materials
Refer to the Orange County Stormwater Program (ocwatersheds.com) for a library of materials
available. For the copy submitted to the Permittee, only attach the educational materials specifically
applicable to the project. Other materials specific to the project may be included as well and must
be attached.
Education Materials
Residential Material
(http://www.ocwatersheds.com)
Check If
Applicable
Business Material
(http://www.ocwatersheds.com)
Check If
Applicable
The Ocean Begins at Your Front Door Tips for the Automotive Industry
Tips for Car Wash Fund-raisers Tips for Using Concrete and Mortar
Tips for the Home Mechanic Tips for the Food Service Industry
Homeowners Guide for Sustainable
Water Use Proper Maintenance Practices for Your
Business
Household Tips Compliance BMPs for Mobile
Businesses
Proper Disposal of Household
Hazardous Waste
Other Material Check If
Attached Recycle at Your Local Used Oil
Collection Center (North County)
Recycle at Your Local Used Oil
Collection Center (Central County)
Recycle at Your Local Used Oil
Collection Center (South County)
Tips for Maintaining a Septic Tank
System
Responsible Pest Control
Sewer Spill
Tips for the Home Improvement Projects
Tips for Horse Care
Tips for Landscaping and Gardening
Tips for Pet Care
Tips for Projects Using Paint
PA2019-142
ATTACHMENT A
PA2019-142
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-24 December 20, 2013
INF-2: Infiltration Trench Fact Sheet
An infiltration trench is a long, narrow, rock-filled trench
with no outlet other than an overflow outlet. Runoff is stored
in the void space between stones and infiltrates through the
bottom and sides of the trench. Infiltration trenches provide
the majority of their pollutant removal benefits through
volume reduction. Pretreatment is important for limiting
amounts of coarse sediment entering the trench which can
clog and render the trench ineffective. Note: if an infiltration
trench is “deeper than its widest surface dimension,” or includes an
assemblage of perforated pipes, drain tiles, or other similar
mechanisms intended to distribute runoff below the surface of the
ground, it would probably be considered a "Class V Injection Well"
under the federal Underground Injection Control (UIC) Program,
which is regulated in California by U.S. EPA Region 9. A UIC
permit may be required for such a facility (for details see
http://www.epa.gov/region9/water/groundwater/uic-classv.html).
Feasibility Screening Considerations
x Infiltration trenches shall pass infeasibility screening criteria to be considered for use
x Infiltration trenches, particularly deeper designs, may not provide significant attenuation of
stormwater pollutants if underlying soils have high permeability; potential risk of groundwater
contamination.
x The potential for groundwater mounding should be evaluated if depth to seasonally high
groundwater (unmounded) is less than 15 feet.
Opportunity Criteria
x Soils are adequate for infiltration or can be amended to provide an adequate infiltration rate.
x Drainage area area is ≤ 5 acres and has low to moderate sediment production.
x 2-3 percent of drainage area available for infiltration (generally requires less surface area than
infiltration basins and bioretention areas without underdrain).
x Space available for pretreatment (biotreatment or treatment control BMP as described below).
x Potential for groundwater contamination can be mitigated through isolation of pollutant sources,
pretreatment of inflow, and/or demonstration of adequate treatment capacity of underlying soils.
x Infiltration is into native soil, or depth of engineered fill is ≤ 5 feet from the bottom of the facility to
native material and infiltration into shallow fill is approved by a geotechnical professional.
x Tributary area land uses include open areas adjacent to parking lots, driveways, and buildings,
and roadway medians and shoulders.
OC-Specific Design Criteria and Considerations
□ Must comply with local, state, and federal UIC regulations if applicable; a permit may be
required.
Also known as:
¾French Drains
¾Rock Trenches
¾Exfiltration Trenches
¾Soak-aways
¾Soakage Trenches
Infiltration Trench
Source: www.dot.ca.gov
PA2019-142
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-25 December 20, 2013
□
Placement of BMPs should observe geotechnical recommendations with respect to geological
hazards (e.g. landslides, liquefaction zones, erosion, etc.) and set -backs (e.g., foundations,
utilities, roadways, etc.)
□ For facilities with tributary area less than 1 acre and less than 3 foot depth, minimum separation
to mounded seasonally high groundwater of 5 feet shall be observed.
□ For facilities with tributary area greater than 1 acre or deeper than 3 feet, minimum separation to
mounded seasonally high groundwater of 10 feet shall be observed.
□ Minimum pretreatment should be provided upstream of the infiltration trench, and water
bypassing pretreatment should not be directed to the infiltration trench.
□ Infiltration trenches should not be used for drainage areas with high sediment production
potential unless preceded by full treatment control with a BMP effective for sediment removal.
□
Ponded water should not persist within 1 foot of the surface of the facility for longer than 72
hours following the end of a storm event (observation well is needed to allow observation of
drain time).
□ Energy dissipators should be provided at inlet and outlet to prevent erosion.
□ An overflow device must be provided if basin is on-line.
□ A minimum freeboard of one foot should be provided above the overflow device (f or an on-line
basin) or the outlet (for an off-line basin).
□ Longitudinal trench slope should not exceed 3%.
□ Side slopes above trench fill should not be steeper than 3:1.
Simple Sizing Method for Infiltration Trenches
If the Simple Design Capture Volume Sizing Method is used to size an infiltration trench, the user
calculates the DCV and then designs the geometry required to draw down the DCV in 48 hours. The
sizing steps are as follows:
Step 1: Determine Infiltration Basin DCV
Calculate the DCV using the Simple Design Capture Volume Sizing Method described in Appendix
III.3.1.
Step 2: Determine the 48-hour Effective Depth
The depth of water that can be drawn down in 48 hours can be calculated using the following equation:
d48 = KDESIGN × SACF × 48 hours
Where:
d48 = trench effective 48-hour depth, ft
KDESIGN = basin design infiltration rate, in/hr (See Appendix VII)
SACF = Surface Area Correction Factor = ranges from 1.0 (sides insignificant or not accounted) to
2.0 (sides plus bottom are 2 times the surface area of the bottom at mid depth) to account for the ratio
of infiltration through the sides of the trench to the bottom footprint of the trench; should be based on
anticipated trench geometry and wetted surface area at mid-depth.
This is the maximum effective depth of the trench below the overflow device to achieve drawdown in 48
hours.
PA2019-142
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-26 December 20, 2013
Step 3: Determine the Trench Ponding Depth and Trench Depth
The depth of water stored in the ponding depth (i.e. above the trench fill) and within the trench itself
should be equal or less than d48. Determine the ponding depth and the trench fill depth such that:
d48 ≥ (nT × dT + dP)
Where:
d48 = trench effective 48-hour depth, ft (from Step 2)
nT = porosity of trench fill; 0.35 may be assumed where other information is not available
dT = depth of trench fill, ft
dP = ponding depth, ft (should not exceed 1 ft)
Step 4: Calculate the Required Infiltrating Area
The required footprint area can be calculated using the following equation:
A = DCV/ ((nT × dT) + dP)
Where:
A = required trench footprint area, sq-ft
DCV = design capture volume, cu-ft (see Step 1)
nT = porosity of trench fill; 0.35 may be assumed where other information is not available
dT = depth of trench fill, ft
dP = ponding depth, ft
Capture Efficiency Method for Infiltration Trenches
If BMP geometry has already been defined and deviates from the 48 hour drawdown time, the designer
can use the Capture Efficiency Method for Volume-Based, Constant Drawdown BMPs (Appendix III.3.2)
to determine the fraction of the DCV that must be provided to manage 80 percent of average annual
runoff volume. This method accounts for drawdown time different than 48 hours.
Step 1: Determine the drawdown time associated with the selected trench geometry
DD = ((nT × dT) + dP) / (KDESIGN × SACF) × 12
Where:
DD = time to completely drain infiltration basin ponding depth, hours
nT = porosity of trench fill; 0.35 may be assumed where other information is not available
dT = depth of trench fill, ft
dP = ponding depth, ft
SACF = Surface Area Correction Factor = ranges from 1.0 (sides insignificant or not accounted) to
2.0 (sides plus bottom are 2 times the surface area of the bottom at mid depth) to account for the ratio
of infiltration through the sides of the trench to the bottom footprint of the trench; should be based on
anticipated trench geometry and wetted surface area at mid-depth.
KDESIGN = basin design infiltration rate, in/hr (See Appendix VII)
Step 2: Determine the Required Adjusted DCV for this Drawdown Time
Use the Capture Efficiency Method for Volume-Based, Constant Drawdown BMPs (Appendix III.3.2) to
calculate the required fraction of the DCV the basin must hold to achieve 80 percent capture of average
annual stormwater runoff volume based on the trench drawdown time calculated above.
PA2019-142
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-27 December 20, 2013
Step 3: Determine the Trench Infiltrating Area Needed
The required footprint area can be calculated using the following equation:
A = DCV / ( (nT × dT) + dP)
Where:
A = required trench footprint area, sq-ft
DCV = design capture volume, cu-ft (see Step 1)
nT = porosity of trench fill; 0.35 may be assumed where other information is not available
dT = depth of trench fill, ft
dP = ponding depth, ft
If the area required is greater than the selected trench area, adjust surface area or adjust ponding and/or
trench depth and recalculate required area until the required area is achieved.
Configuration for Use in a Treatment Train
x Infiltration trenches may be preceeded in a treatment train by HSCs in the drainage area, which
would reduce the required volume of the trench.
x Infiltration trenches must be preceeded by some form of pretreatment which may be biotreatment
or a treatment control BMP; if an approved biotreatment BMP is used as pretreatment, the
overflow from the infiltration trench may be considered “biotreated” for the purposes of meeting
the LID requirments
x The overflow or bypass from an infiltration trench can be routed to a downstream biotreatment
BMP and/or a treatment control BMP if additional control is required to achieve LID or treatment
control requirements
Additional References for Design Guidance
x CASQA BMP Handbook for New and Redevelopment:
http://www.cabmphandbooks.com/Documents/Development/TC-10.pdf
x SMC LID Manual (pp 141):
http://www.lowimpactdevelopment.org/guest75/pub/All_Projects/SoCal_LID_Manual/SoCalL
ID_Manual_FINAL_040910.pdf
x Los Angeles County Stormwater BMP Design and Maintenance Manual, Chapter 6:
http://dpw.lacounty.gov/DES/design_manuals/StormwaterBMPDesignandrainage
areaintenance.pdf
x City of Portland Stormwater Management Manual (Soakage Trenches, page 2-82)
http://www.portlandonline.com/bes/index.cfm?c=47954&a=202883
x San Diego County LID Handbook Appendix 4 (Factsheet 1):
http://www.sdcounty.ca.gov/dplu/docs/LID-Appendices.pdf
PA2019-142
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-74 December 20, 2013
TRT-2: Cartridge Media Filter
Cartridge media filters (CMFs) are manufactured devices that
consist of a series of modular filters packed with engineered
media that can be contained in a catch basin, manhole, or
vault that provide treatment through filtration and
sedimentation. The manhole or vault may be divided into
multiple chambers where the first chamber acts as a pre-
settling basin for removal of coarse sediment while another
chamber acts as the filter bay and houses the filter cartridges.
A variety of media types are available from various
manufacturers which can target pollutants of concern.
Feasibility Screening Considerations
x Not applicable
Opportunity Criteria
x Intended for use when retention and biotreatment options are infeasible.
x Recommended for drainage area with limited available surface area or where surface BMPs
would restrict uses.
x For drainage areas with significant areas of non-stabilized soil, permanent soil stablization must
be achieved before before cartridge media filters are installed and put on line to minimize risk of
clogging.
x Depending on the number of cartridges, maintenance events can have long durations. Care
should be exercised in siting these facilities so that maintenance events will not significantly
disrupt businesses or traffic.
OC-Specific Design Criteria and Considerations
□ Cartridge media filter BMP vendors should be consulted regarding design and specifications.
□ Filter media should be selected to target pollutants of concern. A combination of media may be
appropriate to remove a variety of pollutants.
□ If CMF are integrated with a vault for equalization, the system should be designed to completely
drain the vault within 96 hours of storm event or otherwise protect aga inst standing water and
mosquito breeding concerns.
Computing Sizing Criteria for Cartridge Media Filters
The required design flowrate should be calculated based on the Capture Efficiency Method for Flow-
based BMPs (See Appendix III.3.3).
Additional References for Design Guidance
x Los Angeles County Stormwater BMP Design and Maintenance Manual, Chapter 9:
http://dpw.lacounty.gov/DES/design_manuals/StormwaterBMPDesignandMaintenance.pdf
Cartridge Media Filter
Source: Contech Stormwater
Solution, Inc.
Also known as:
¾Manufactured Media
Filters
PA2019-142
TECHNICAL GUIDANCE DOCUMENT APPENDICES
XIV-75 December 20, 2013
x SMC LID Manual:
http://www.lowimpactdevelopment.org/guest75/pub/All_Projects/SoCal_LID_Manual/SoCalL
ID_Manual_FINAL_040910.pdf
x Western Washington Stormwater Management Manual, Volume V, Chapter 12:
http://www.ecy.wa.gov/pubs/0510033.pdf
PA2019-142
Submittal Package
FLOGARD® CATCH BASIN INSERT FILTER
PA2019-142
1 - Features & BeneFits
2 - accessories
3 - Product sPeciFications
table of contentS
PA2019-142
Features & BeneFits
Section 1
PA2019-142
Call us today (800) 579-8819 or visit our website for detailed product information, drawings and
design tools at www.oldcastlestormwater.com
FLOGARD® CATCH BASIN INSERT FILTER
INLET FILTRATIONRemoves Pollutants from Runoff Prior to Entering Waterways
Efficient System
Catches pollutants where they
are easiest to catch, at the inlet.
Focused Treatment
Removes petroleum hydro-
carbons, trash and Total
Suspended Solids (TSS).
Variable Design
Able to be retrofitted or
used in new projects.
Two-part stainless-steel
insert to filter solids and
oils/grease
Easy to install, inspect and maintain, even on small and confined sites
Treatment Train
Can be incorporated as
part of a “Treatment Train”.
No Standing Water
Helps to minimize bacteria
and odor problems.
Economical
Earn a higher return on
system investment.
Maximum Flexibility
Available in a variety of standard
sizes to fit round and square inlets.
Catch Basin Filter Test Results Summary
UCLA
U of Auckland
Tonking & Taylor, Ltd.
(for City of Auckland)
U of Hawaii
(for City of Honolulu)
80
78 to 95
80
70 to 80
Testing Agency % TSS Removal % Oil & Grease Removal
20 to 40
% PAH Removal
By the Numbers*:
Filter will remove up to 80% of Total
Suspended Solids (TSS), at least 70%
of oils and grease and 40% of Total
Phosphorus (TP) associated with
organic debris as well as Polycyclic
Aromatic Hydrocarbons (PAH ) from oil
leaks and spills.
*Approx. for urban street application
PA2019-142
(800) 579-8819
oldcastlestormwater.com © 2017 Oldcastle Precast, Inc.
OSS_FloGard CBIF Insert_032017_v4
Multi-Purpose Catch Basin Insert Retains Sediment, Debris, Trash and Oils/Grease
FloGard® Catch Basin Insert Filters are recommended for areas subject to silt and debris as well as low-to-moderate
levels of petroleum hydrocarbons (oils and grease). Examples of such areas include vehicle parking lots, aircraft ramps,
truck and bus storage yards, business parks, residential and public streets.
Catch Basin Filter Competitive Feature Comparison
Evaluation of Catch Basin Filters Oldcastle Stormwater Other Insert Filter Types**
(Based on flow-comparable units) (Scale 1-10)
Flow Rate 10 7
Removal Efficiency* 80% 45%
Capacity - Sludge & Oil 7 7
Service Life 10 3
Installation - Ease of Handling / Installation 8 6
Ease of Inspections & Maintenance 7 7
Value 10 2
*approximate, based on field sediment removal testing in urban street application **average
Long-Term Value Comparison Oldcastle Stormwater Other Insert Filter Types
(Based on flow-comparable units) (Scale 1-10)
Unit Value - Initial ($/cfs treated) 10 4
Installation Value ($/cfs treated) 10 7
Absorbent Replacement (annual avg ($/cfs treated) 10 2
Materials Replacement Value (annual avg ($/cfs treated) 10 10
Maintenance Value (annual avg ($/cfs treated) 10 7
Total First Year ROI ($/cfs treated) 10 5
Total Annual Avg Value ($/cfs treated, avg over 20 yrs)* 10 5
Flat-Grated Inlet
Circular Frame Catch BasinCaptured debris from FloGard Catch Basin Insert Filter in Dana Point, California
Combination Inlet
PA2019-142
accessories
Section 2
PA2019-142
U.S. PATENT #6,551,023 & 6,872,029
FloGard ® FILTER
-INSTALLED INTO CATCH BASIN-
GRATE ----1'«
"ULTIMATE" BYPASS FEATURES
STAINLESS STEEL SUPPORT BASKET
Fossil Rock'" ABSORBENT POUCHES ~
LINER ----
SUPPORT BASKET ---
CATCH BASIN (FLAT C:AATE STYLE)
NOTES:
DETAIL A
EXPLODED VIEW
1.
2
Filter insert shall have a high flow bypass feature.
3.
4.
Filter support frame shall re constructed from stainless steel
Type 304.
Filter medium shall re Fossil Rock installed and maintained h
accordance with manufacturer specifications.
Storage capacity reflects W /o of maximum solids collection prior
to impeding filtering bypass.
PA2019-142
Product sPeciFications
Section 3
PA2019-142
STANDARD
DEPTH
INLET ID
Inside
Dimension
(inch x inch)
GRADE OD
Outside
Dimension
(inch x inch)
TOTAL
BYPASS
CAPACITY
(cu. ft. / sec.)
SOLIDS
STORAGE
CAPACITY
(cu. ft.)
FILTERED
FLOW
(cu. ft. / sec.)
SHALLOW
DEPTH
SOLIDS
STORAGE
CAPACITY
(cu. ft.)
FILTERED
FLOW
(cu. ft. / sec.)
FGP-1633FGO 16 X 33 18 X 36 7.0 2.5 1.7 FGP-1633FGO8 1.4 1.1
FGP-1836FGO 18 X 36 18 X 40 6.9 2.3 1.6 FGP-1836FGO8 1.3 .9
FGP-2234FGO 22 X 34 24 X 36 8.1 3.6 2.1 FGP-2234FGO8 2.1 1.4
FGP-2436FGO 24 X 36 24 X 40 8.0 3.4 2.0 FGP-2436FGO8 1.95 1.15
STANDARD
DEPTH
INLET ID
Inside
Dimension
(inch x inch)
GRADE OD
Outside
Dimension
(inch x inch)
TOTAL
BYPASS
CAPACITY
(cu. ft. / sec.)
SOLIDS
STORAGE
CAPACITY
(cu. ft.)
FILTERED
FLOW
(cu. ft. / sec.)
SHALLOW
DEPTH
SOLIDS
STORAGE
CAPACITY
(cu. ft.)
FILTERED
FLOW
(cu. ft. / sec.)
FGP-12F 12 X 12 12 X 14 2.8 0.3 0.4 FGP-12F8 .15 .25
FGP-16F 16 X 16 16 X 19 4.7 0.8 0.7 FGP-16F8 .45 .4
FGP-18F 18 X 18 18 X 20 4.7 0.8 0.7 FGP-18F8 .45 .4
FGP-1836F 18 X 36 18 X 40 6.9 2.3 1.6 FGP-1836F8 1.3 .9
FGP-21F 22 X 22 22 X 24 6.1 2.2 1.5 FGP-21F8 1.25 .85
FGP-24F 24 X 24 24 X 27 6.1 2.2 1.5 FGP-24F8 1.25 .85
FGP-2436F 24 X 36 24 X 40 8.0 3.4 2.0 FGP-2436F8 1.95 1.15
FGP-2448F 24 X 48 24 X 48 9.3 4.4 2.4 FGP-2448F8 2.5 1.35
FGP-32F-TN 28 X 28 32 X 32 6.3 2.2 1.5 FGP-32F8-TN 1.25 .85
FGP-30F 30 X 30 30 X 34 8.1 3.6 2.0 FGP-30F8 2.05 1.15
FGP-36F 36 X 36 36 X 40 9.1 4.6 2.4 FGP-36F8 2.65 1.35
FGP-3648F 36 X 48 40 X 48 11.5 6.8 3.2 FGP-3648F8 3.9 1.85
FGP-48F 48 X 48 48 X 54 13.2 9.5 3.9 FGP-48F8 5.45 2.25
FGP-1633F 16 X 34 18 X 36 6.9 2.3 1.6 FGP-1633F8 1.3 .9
FGP-2234F 22 X 34 24 X 36 8.0 3.4 2.0 FGP-2234F8 1.95 1.15
STANDARD DEPTH
-20 Inches-
SHALLOW DEPTH
-12 Inches-
FloGard Combination Inlet
SPECIFIER CHART
STANDARD & SHALLOW
DEPTH
(Data in these columns is the same for
both STANDARD & SHALLOW versions)MODEL NO.MODEL NO.
FloGard Flat Grated Inlet
SPECIFIER CHART
STANDARD & SHALLOW
DEPTH
(Data in these columns is the same for
both STANDARD & SHALLOW versions)
STANDARD DEPTH
-20 Inches-
SHALLOW DEPTH
-12 Inches-
MODEL NO.MODEL NO.
U.S. PATENT #6,551,023 & 6,872,029
* MANY OTHER STANDARD & CUSTOM SIZES AND DEPTHS AVAILABLE UPON REQUEST.
PA2019-142
INLET, FRAME & GRATE INFORMATION
CONTACT INFORMATION
CONTACTDETAILSCompany:
Job Name:
Job Address:
Contact Name:
Email:TYPEInlet Type (e.g. PA Type M):
Frame Model #:
Grate MFG/Model (e.g. Neenah R-2060):
Grate Type (Check One): Cast Iron Steel
PLEASE PROVIDE MEASUREMENTS WITHIN 1/8" TO GUARANTEE ACCURATE INSTALLATION*
THE FOLLOWING MEASUREMENTS ARE REQUIRED TO PLACE AN ORDER
Notes: If any obstructions or protrusions exist within the catch basin, please provide photos and accurate measurements to ensure proper installation. Submittal
of this form represents that the customer acknowledges that all details provided are accurate, and that any issues resulting from inaccurate information herein are
the responsibility of said customer. * Use second page for additional catch basins.
CONTACT INFORMATION
Grate
Grate outside dimensions
A
Grate outside dimensions
B
Catch Basin
Frame clear opening or
wall to wall inside the
catch basin, whichever
is less
C
Frame clear opening or
wall to wall inside the
catch basin, whichever
is less
D
Grate section
Square belly
Round belly
Flat
Section through Catch Basin
Bottom of frame to top
of outlet pipe
E
Bottom of frame to
floor of catch basin
F
Grate type (pick one):
Belly width
Belly width
Belly depth
Belly depth
G
H
I
J
City/State/Zip:
Phone:
Pipe inside diameterDo you have inlet pipes?If yes, bottom of grate to top of pipeYN Need to be filtered?Y N
Inlet Pipes?
Please email completed forms to contactstormwater@oldcastle.com
www.oldcastlestormwater.com Phone: (800) 579-8819
Measurement Chart for FloGard Inserts
(Square/Rectangular Flat Grated Inlets)
PA2019-142
PLEASE PROVIDE MEASUREMENTS WITHIN 1/8" TO GUARANTEE ACCURATE INSTALLATION
A - Grate outside dimensions
B - Grate outside dimensions
C - Frame clear opening or wall to wall inside the catch basin, whichever is less
D - Frame clear opening or wall to wall inside the catch basin, whichever is less
E - Measure from bottom of frame to top of outlet pipe
F - Bottom of frame to floor of catch basin
* If grate has "belly" please include measurements for G & H or I & J, depending
on belly style.
Notes: If any obstructions or protrusions exist within the catch basin, please provide photos and accurate measurements to ensure proper installation. Submittal
of this form represents that the customer acknowledges that all details provided are accurate, and that any issues resulting from inaccurate information herein are
the responsibility of said customer.
THE FOLLOWING MEASUREMENTS ARE REQUIRED TO PLACE AN ORDER
Bottom of frame
to top of pipeGrate outside dimensions Frame clear opening or wall to
wall inside the catch basin
A B C D E F
Bottom of frame to
floor of catch basinQuantity/
Drain #
Square belly
width
G H I J
Square belly
depth Round belly
width Round belly
depth
Square belly grate Round belly grate
Please email completed forms to contactstormwater@oldcastle.com
www.oldcastlestormwater.com Phone: (800) 579-8819
Measurement Chart for FloGard Inserts
(Square/Rectangular Flat Grated Inlets)
NOTES:
PA2019-142
www.oldcastlestormwater.com
800-579-8819
BUILDING
STRUCTURES
OUR MARKETS
TRANSPORTATION
WATER
ENERGYCOMMUNICATIONS
FLOGARD® CATCH BASIN INSERT FILTER
PA2019-142
ATTACHMENT B
PA2019-142
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w,,•w.ciwnlb.ca..go,•
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AssCSS1nen1
www.ochha.ca.gcw
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www.w;.uerboards.ca.gO\I
Earth 911 .Co11ununit)'-{jpccific En,'1 ron111tn lal
l nfom)alivn 1-800-dcanup or vi.sit www. J800de:mup,
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Huh.h Cue ARenc)"s Ocean and Bay Water Closure
and Poi.ling Hotline
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ln1egra1ed Waste Mlllllagemeot Depc. of Orange
County (714) 83,1-6752 0( \'iS il W"iW.oclandfilli.COlll for
information on howchold ha1.3.rdow "-'a.Ste coUcction
ccntcn, recycling ccoten and solid wane coUection
O.C. ~culture Commj,..;ooer
(714) 447-7100 orvitil """'.ocagtamm.com
Stormwa1er Be.t Management Pn.ctice Hmdbook
,ruit www.cabrnphandbooks.com
UC Muter Gardeoer Hotlla.e
(714) 70S-1646 onui1 www.ucccmg.com
The Or.rnge County Stormwat.er Program 1w created
and modcratca an clcef.tonic mailing tut to facilitilc
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il.1 wen about i.uuca a.nd topic, related 10 11onnwa1cr and
w-ba.n runoff and the lmplCtUcntadon uf prugn,m clcwcr1u.
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oatonm•r4terinf0joinelltt.o<:wa;tcl')hcds.curn
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Or.mgc County StormW',Ucr Program ...••.. (877) 897•7'455
Orange County 2-Ulour
¥.r,,1cr Pollv.1ion Problem RcpurUng Hotline
1-817-89-SPILL (1-877-897-7455)
On-tine Water PoUution Problem Reponing torm
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PA2019-142
Follow Lhcse s implesLeps to help reduce waler
poll uLion :
Household Activities
a oo not rinse sp ill s wiLh water. Use dry cleanup
methods such as applying cat liner or another
absorbent matc,ial, sweep and dispose of in
t he trash. Take items such as used or excess
baltctics, oven cleaners, a.utomol.ivc fluids,
painting producLS a n d ca1hodc ray tubes, li ke
TVs and computei· m onilors, to a J l ouschold
I lazardous Waste Collection Center ( 111 lWCC).
•Fora H HWCC near you call ( 714 > 83-H; 752 or
visi1 ,,ww.oclandfi1ls.com .
• Oo 1'IOt hose down rour dri\'cwar, sidewalk or
patio to the street, guucr or stonn drain. Sweep
up debris and d ispose ofiL in the trash.
Automotive
•Take your vehicle to a commercial car
wash whc,,cvcr possible. l(' you wash your
ve hic le at home, choose soaps, cleaners, or
deLcrgcnts labeled non-toxic, phosphate-free
or biodegradable. VcgcLab lc and c iLrus-bascd
products arc typicall y safesL for Lhc environment.
• Do not allow washwatcr from vehicle washi ng
lO drain hno t he su·cet, gutter ot storm drain.
Excess was hw:ucrshould be disposed of in the
sanitary sewer (through a sink. or toilet) or onto
an absotbcm surrace li ke your lawn.
•MoniLOr your vehicles for leaks and p lace a pan
under lc;1ks. Keep your vehicles well main tained
LO stop and prc,.cot leaks.
a Never pour oil or antifreeze in the street, gutter
or sto1m drain. Recycle these subsc...·rnccs at a
service Slation, a waste o il collection center o r
used oil recycling center. For t11c nearcsL Used
Oil Collection Center call 1-800-CI.EANUP or
visit \,ww. l800clc~11mp.o rg.
Pool Maintenance
•Pool a nd spa wa ter must be dechlorinated a nd free
of excess acid, alkali or color LO be allowed in the
su·cet, guuer or stonn drain.
•\<Vheo it i.s oot raining, drain dechlorinated pool and
spa \Yc\Ler di1·ectly into the
sanitary sewer.
•Some cities may have ordinances that do not allow
pool ,.,.1cr 10 be disposed of in the stoi,n drain.
Check with your city.
Landscape and Gardeui11g
• Do 110L over-water. Water your lawn and garden by
hand to control the amount of water you use or set
i1 l'igation systems to rdlcc1 scasoual water needs .
tr wa ter flows off your yc1.nl onto your driveway 01
side"alk, your S)'Stcm is ovCM\'atcring. Pc1iodically
inspcc1 and r.~ kak:. ctnd 111i~di1l:1.-t1:d sp1i11l,,.k1:,,
• Do IIOL rake or b low leaves, c lippings or pruning
waste into the street, gutter or storm drain. lnstcad .
dispose of waste by composting, hauling it LO a
p<·1'111i1ted lan<llill , nr as g 1·,·(•n waue.~ 1hro11gh ymn
city's recycling program.
• 1-"ollow directions on pestic ides and fertil izer.
(measu re. do not estimate amounts) and do not use
if rain is predicted within 48 hours.
•·rake unwanted pesticides 10 a I IHWCC Lo be
recycled. For locations a nd hours of HHWCC, call
(714) 8346752 or visiL """·ocl;u1dfill.s.com.
Trash
a Place trash and liner t hal can not be recycled in
securel)' covered lrash cans.
•w henever possible, buy recycled producu.
• Remember: Reduce, Reuse, Recycle.
Pet Care
•Always pick up afier your pct. l'lush waste down
the toilet or dispose ofiL in the ,rash. Pct waste,
if left outdoors, can wash imo the street, gutter
or stonn drain.
• If possible, bathe your pets indoors. If you must
bathe your pe1 outside, wash it on your lawn or
anoth er absorbcnt/penneable surface to keep
the waslw,•.uer from cmering the street, gutter or
stonn drain.
•Follow direcli o ns for use of pct cal"e products
and cli..sp<»c of any u n u.:scd pnxlucu al a
HHWCC.
PA2019-142
For m o re information ,
p l ease call the
Orange County Stormwate r Program
a t 1-877-89-SPILL (1 -8 7 7-89 7-7 455)
or visit
www.ocwatersheds.com
To Report lliegal Dumping o f
Household Hazardous Waste
call 1-800-69-TOXIC
To r e p ort a spill ,
call t h e
Orange County 24-Hour
Water Pollution Problem
R e port ing Hotline
1-877-89-SPILL (1-8 77-89 7-7455).
For emergencies, dial 911.
' Rl':CYCLE
USED0 J t .~ ... ••T
P1i11te d o n Reqcl e <l Pape r
PROJECT
Po33ut,on
PREVENTION
PA2019-142
Leftover household products that contain
corrosive, toxic, ignitable, or reactive
\VI 1/:N POSS/BU:.
l 'SI :·
.V0/\1-//J\'h\Ul)OlT.\
OU
IFSS-I IA'/AIU>Ol TS
PUO/Jl 1CIX
ingredients are
considered to
be "household
hazardous waste"
or "HHW." HHW
can be found
throughout your
home, including the
bathroom, kitchen,
laundry room and
garage.
Disposal of HHW down the drain, on the
ground, into storm drains, or in the trash
is illegal and unsafe.
Proper disposal of HHW is actually easy.
Simply drop them off at a Household
Hazardous Waste Collection Center
(HHWCC) for free disposal and recycling.
Many materials including anti-freeze, latex-
based paint, motor oil and batteries can
be recycled. Some centers have a "Stop &
Swap" program that lets you take partially
used home, garden, and automobile
products free of charge. There are four
HHWCCs in Orange County:
Anaheim: .................. 1071 N. Blue Gum St
Huntington Beach: ......... 17121 Nichols St
Irvine: ............................ 6411 Oak Canyon
Sanjuan Capistrano: ... 32250 La Pata Ave
Centers are open Tuesday-Saturday, 9 a.m.-
3 p.m. Centers are closed on rainy days and
major holidays. For more information, call
(714) 834-6752 or visit www.oclanclfills.com.
Cornman household hazardous
wastes
• Batteries
• Paint and paint products
• Adhesives
• Drain openers
• Household cleaning products
• Wood and metal cleaners and polishes
• Pesticides
• Fungicides/wood preservatives
• Automotive products (antifreeze, motor
oil, fluids)
• Grease and rust solvents
• Fluorescent lamps
• Mercury (thermometers & thermostats)
• All forms of electronic waste including
computers and microwaves
• Pool & spa chemicals
• Cleaners
• Medications
• Propane ( camping & BBQ)
• Mercury-containing lamps
• Television & monitors (CRTs,
flatscreens)
Tips for household hazardous
waste
• Never dispose of HHW in the trash,
street, gutter, storm drain or sewer.
• Keep these materials in closed, labeled
containers and store materials indoors
or under a cover.
• When possible, use non-hazardous
products.
• Reuse products whenever possible or
share with family and friends.
• Purchase only as much of a product as
you'll need. Empty containers may be
disposed of in the trash.
• HHW can be harmful to humans,
pets and the environment. Report
emergencies to 911.
PA2019-142
For m ore informatio n ,
ple a se call the
Orange County Stormwater Program
a t 1-877-89-SPILL (1-87 7-89 7-7455)
or vis it
www.ocwatersheds.com
UCCE Master Gardener Hotline:
(714) 708-1646
To report a s pill ,
c a ll the
Orange County 24-Hour
Water Pollution Problem
Reporting Hotline
1-877-89-SPILL (1 -8 77-89 7-7 455).
For emergencies, dial 911.
The ti p s contained in this brochure provide 11sefol
informati on to h elp preven t wa ter poll ution
while landscaping or gardening. If you have other
suggestions, please-contact your c ity's stormwater
representatives or call the O range County
Stormwater Program .
• #\.
••"'
R O J I
PA2019-142
Never allow gardening products or
polluted water to enter the street, gutter
or storm drain.
General Landscaping Tips
• Protect stockpiles and materials from
wind and rain by storing them under
tarps or secured plastic sheeting.
•Prevent erosion of slopes b y planting
fast-growing, dense ground covering
plants. These will shield and bind the
soil.
•Plant native vegetation
to reduce the amount
of water, fertili zers, and
pesticide applied to the
landscape.
•Never apply pesticides
or fertilizers when rain is
predicted within the next 48 hours.
Garden & Lawn Maintenance
•Do not overwater. Use irrigation
practices such as drip irrigation,
soaker hoses or micro spray systems .
Periodically inspect and fix leaks and
misdirected sprinklers.
• Do not rake or blow
leaves, clippings or
pruning waste into
the street, gutter
or storm drain.
Instead, dispose
of green waste by
composting, hauling
it to a permitted
landfill, or recycling it through your
city's program.
• Use slow-release fertilizers to
minimize leaching, and use organic
fertili zers.
• Read labels and use only as directed.
Do not over-apply pesticides or
fertilizers. Apply to spots as needed,
rather than blanketing an entire
area.
• Store pesticides, fertilizers and other
chemicals in a dry covered area to
prevent exposure that may result
in the deterioration
of containers and
packaging.
• Rinse empty
pesticide containers
and re-use rinse water
as you would use the
product. Do not dump rinse water
down storm drains. Dispose of empty
containers i n the trash.
•When available, use non-toxic
alternatives to traditional pesticides,
and use pesticides specifi cally
designed to control the pest you are
targeting. For more information, visit
www.ipm.ucdavis.edu.
• If fertilizer is spilled, sweep up th e
spill before irrigating. If the spill is
liquid, apply an absorbent material
such as cat litter, and then sweep i t up
and dispose of i t in the trash.
• Take unwanted pesticides to a
Household Hazardous Waste
Collection Center to be recycled.
Locations are provided below.
PA2019-142
For m o r e infor mation,
p lease call t h e
Orange County Stormwater P rogram
at 1-877-89-SPILL (1 -877-897-7455)
or visit
www.ocwate rshe ds.com
To r e p ort a spill ,
call the
Orange County 24-Hour
Water Pollution Reporting Hotline
1-877-89-SPILL (l-8 77-897-7455).
For emergencie s, dial 911.
The tips contained in this brochure provide useful
information to help prevent water pollution
while maintaining your pool. If you have other
suggestions, please contact your city's stonnwatcr
representatives or call the Orange County
Stormwatcr Program.
Tli e Ocean Begins
at Your Front Door
PROJECT
Poii~t,on
_P R E V E N ,T-I O N
PA2019-142
Many pools are
plumbed to allow the
pool to drain directly
to the sanitary sewer.
If yours is not, follow
these instructions for
disposing of pool and
spa water.
f
Acceptable and Preferred
Method of Disposal
When you cannot dispose of pool water
in the sanitary sewer, the release of
dechlorinated swimming pool water is
allowed if all of these tips are followed:
• The residual chlorine does not
exceed 0.1 mg/1 (parts per million).
•The pH is between 6.5 and 8 .5 .
•The water is free of any unusual
coloration, dirt or algae.
• There is no discharge of filter media.
• There is no discharge of acid
cleaning wastes.
• Some cities may have ordinances
that do not allow pool water to be
disposed into a storm drain. Check
with your city.
How t o Know if You 're
Following the Standards
You can find out how much chlorine
is in your water by using a pool testing
kit. Excess chlorine can be removed
by discontinuing the use of chlorine
for a few days prior to discharge
or by purchasing dechlorinating
chemicals from a l ocal pool supply
company. Always make sure to follow
the instructi ons that come with any
products you use.
Doi ng Your Part
By complying with these guidelines,
you will make a significant contribution
toward keeping pollutants out of
Orange County's creeks, streams, rivers,
bays and the ocean. This helps to
protect organisms that are sensitive to
pool chemicals, and helps to maintain
the health of our environment.
PROJl<T
P0 Hut1 0 11
PA2019-142
ATTACHMENT C
PA2019-142
Operations and Maintenance (O&M) Plan
for
CAMPBELL RESIDENCE
605 VIA LIDO SOUD
Newport Beach, California 92663
APN 423-247-02
Overall Responsible Party/Owner:
MS. BRIDGET CAMPBELL
605 Via Lido Soud
Newport Beach, CA 92663
Contact: Rosie Ou (949) 720-7022
PA2019-142
Exhibit B, Operations and Maintenance Plan
BMP Applicable? Yes/No
BMP Name and BMP Implementation, Maintenance and Inspection Procedures Implementation, Maintenance, and Inspection Frequency and Schedule Person or Entity with Operation & Maintenance Responsibility
Non-Structural Source Control BMPs
Yes
N1. Education for Property Owners, Tenants and Occupants
Practical information materials will be provided to the first
residents/occupants/tenants on general housekeeping
practices that contribute to the protection of stormwater
quality. These materials will be initially developed and
provided to first residents/occupants/tenants by the
developer.
Owner shall keep up to date with BMP
requirements, and be responsible for educating
maintenance personnel; As required.
Owner
No N2. Activity Restrictions
Yes
N3. Common Area Landscape Management
Identify on-going landscape maintenance requirements that
are consistent with those in the County Water Conservation
Resolution (or city equivalent) that include fertilizer and/or
pesticide usage consistent with Management Guidelines for
Use of Fertilizers (DAMP Section 5.5). Statements regarding
the specific applicable guidelines must be included in the
project WQMP.
Keep garden areas clean, planted, and weed free.
Weekly.
Owner or contracted maintenance
personnel
Yes
N4. BMP Maintenance
The project WQMP shall identify responsibility for
implementation of each non-structural BMP and scheduled
cleaning and/or maintenance of all structural BMP facilities.
Visual Inspection, perform more thorough
inspection if ponding water sits for more than 48
hours. Twice yearly and immediately following
each storm event.
Owner or contracted maintenance
personnel
No N5. Title 22 CCR Compliance
No N6. Local Water Quality Permit Compliance
No N7. Spill Contingency Plan
No N8. Underground Storage Tank Compliance
No N9. Hazardous Materials Disclosure Compliance
No N10. Uniform Fire Code Implementation
PA2019-142
Exhibit B, Operations and Maintenance Plan
Page 2 of 7
BMP Applicable? Yes/No
BMP Name and BMP Implementation, Maintenance and Inspection Procedures Implementation, Maintenance, and Inspection Frequency and Schedule Person or Entity with Operation & Maintenance Responsibility
Yes
N11. Common Area Litter Control
The owner may contract with their landscape maintenance
firms to provide this service during regularly scheduled
maintenance, which should consist of litter patrol, emptying
of trash receptacles in common areas, and noting trash
disposal violations by tenants/homeowners or businesses
and reporting the violations to the owner/POA for
investigation.
Keep site clean of litter. Weekly. Owner or contracted maintenance
personnel
No N12. Employee Training
No N13. Housekeeping of Loading Docks
Yes
N14. Common Area Catch Basin Inspection
The owner is required to have at least 80 percent of drainage
facilities inspected, cleaned and maintained on an annual
basis with 100 percent of the facilities included in a two year
period. Cleaning should take place in the late summer/early
fall prior to the start of the rainy season. Drainage facilities
include catch basins (storm drain inlets), detention basins,
retention basins, sediment basins, open drainage channels
and lift stations. Records should be kept to document the
annual maintenance.
Inspect drain inlets and catch basins. Keep inlet
covers clean. Weekly.
Owner or contracted maintenance
personnel
No N15. Street Sweeping Private Streets and Parking Lots
Structural Source Control BMPs
Yes
S1. Provide Storm Drain System Stenciling and Signage
Provide stenciling or labeling of all storm drain inlets and
catch basins, constructed or modified, within the project area
with prohibitive language and/or graphical icons, which
discourage illegal dumping.
Ensure that all catch basins are stencilled “No
Dumping – Drains To Ocean.”
Owner or contracted maintenance
personnel
No S2. Design Outdoor Hazardous Material Storage Areas to Reduce Pollutant Introduction
PA2019-142
Exhibit B, Operations and Maintenance Plan
Page 3 of 7
BMP Applicable? Yes/No
BMP Name and BMP Implementation, Maintenance and Inspection Procedures Implementation, Maintenance, and Inspection Frequency and Schedule Person or Entity with Operation & Maintenance Responsibility
Yes
S3. Design Trash Enclosures to Reduce Pollutant Introduction
Design trash storage areas to reduce pollutant introduction.
All trash container areas shall be paved with an impervious
surface, designed not to allow run-on, screened or walled to
prevent off-site transport of trash, and be provided with a roof
or awning to prevent direct precipitation.
Keep trash storage areas clean and orderly.
Weekly.
Owner or contracted maintenance
personnel
Yes
S4. Use Efficient Irrigation Systems and Landscape Design
Projects shall design the timing and application methods of
irrigation water to minimize the runoff of excessive irrigation
water into the municipal storm drain system. Additionally,
permittee shall: Employ rain shutoff devices, design irrigation
systems to each landscape areas specific requirements, use
flow reducers, group plants with similar water requirements
together.
Ensure that sprinklers are working properly and
minimize unnecessary irrigation. Weekly.
Owner or contracted maintenance
personnel
No S5. Protect Slopes and Channels
No S6. Loading Dock Areas
No S7. Maintenance Bays and Docks
No S8. Vehicle Wash Areas
No S9. Outdoor Processing Areas
No S10. Equipment Wash Areas
No S11. Fueling Areas
No S12. Site Design and Landscape Planning
No S13. Wash Water Controls for Food Preparation Areas
No S14. Community Car Wash Racks
PA2019-142
Exhibit B, Operations and Maintenance Plan
Page 4 of 7
BMP Name and BMP Implementation, Maintenance and Inspection Procedures Implementation, Maintenance, and Inspection Frequency and Schedule Person or Entity with Operation & Maintenance Responsibility
Low Impact Development BMPs
Filter Insert (Treatment). TRT-2
• Filter Insert Replacement/Rotation
• Remove Sediment and debris.
• Once a year. Refer to Manufacturer’s O&M plan on pages 36-39 for details.
• Three times per year and after storm events. Refer to Manufacturer’s O&M plan on pages 36-39 for details.
Owner via maintenance contractors
Infiltration Trench (Biotreatment). INF-2
And Bottomless Trench Drain
• Visual inspection for debris, standing water.
• Gravel/media replacement.
• Filter fabric Replacement
• Twice yearly and after each storm event.
• Every 10 years as required.
• Once a year as required.
Owner via maintenance contractors
PA2019-142
Exhibit B, Operations and Maintenance Plan Attachments
PA2019-142
EXCHA.1.'IGE AND DISPOSAL OF E.\'.POSED FILTER MEDIU AND COLLECTED DEBRIS
The fr equency of' li lt er m edi w11 pouch exchange will be in accor dance with th e existin g DPS-Customer
Maintenance Contract. DPS recom m ends that the m edium be changed at least once per year. During the
a ppropriate service, or if so determined by the service technician dur ing a n cn-schedulecl ser vice, the fi lter
medium pouches w ill be r e placed with new pouches and the exposed pouch es placed in the DOT a pproved
container, along with the exposed debris. Once the exposed pouches and lebris have been placed in the
conta iner, DPS has possess ion and m ust dispose of it in accorda nce w ith local, state an d fede r al agen cy
requirements.
Note: As the generator, the landowner is ultimately respo11siblefor the proper di~po sal of the exposed
filt er medium a/Zll debris. Because the materials likely C{)lztai11 petroleum hy tlro ca rb1J11~·, heavy m etals
and other harmful polluta11ts, tire materials must be treated as an EPA Cla ss 2 Hazardous Waste a11d
properly di~pose tl of. DPS relieves the landow11er of the actual disposal /a$k, anti provides certificalio11
of its c1)111pletio11 i11 accorda11ce with appropriate regulations.
DPS also has the capability or servicing ,lll manner or c,ltch basin inserts and catch b.lsins without.
inserts, underground oil /water separators, storm water interce ptors and other such devices . All DPS
personnel a rc highly qualified technician., and arc confined space trained and certified. Call us at
(888) 950-8826 for rurthcr inform ation and assistance.
PA2019-142
Required Permits
This section must list any permits required for the implementation, operation, and maintenance
of the BMPs. Possible examples are:
• Permits for connection to sanitary sewer
• Permits from California Department of Fish and Game
• Encroachment permits
If no permits are required, a statement to that effect should be made.
Forms to Record BMP Implementation, Maintenance, and Inspection
The form that will be used to record implementation, maintenance, and inspection of BMPs is
attached.
Recordkeeping
All records must be maintained for at least five (5) years and must be made available for review
upon request.
PA2019-142
RECORD OF BMP IMPLEMENTATION, MAINTENANCE, AND INSPECTION
Today’s Date:
Name of Person Performing Activity
(Printed):
Signature:
BMP Name (As Shown in O&M Plan) Brief Description of Implementation, Maintenance, and Inspection Activity Performed
PA2019-142