HomeMy WebLinkAboutMS 15-02; CARLSBAD LAGOON CUSTOM HOMES; HYDROLOGY STUDY FOR CARLSBAD LAGOON BEACH HOMES; 2016-02-09HYDROLOGY STUDY
FOR
CARLSBAD LAGOON BEACH HOMES
165 CHINQUAPIN AVENUE
Grading Permit / Parcel Map
PUD 15-04 / SDP 15-03 I MS 15-02
CITY OF CARLSBAD, CA
PREPARED FOR:
RINCON REAL ESTATE GROUP, INC.
1520 N. EL CAMINO REAL, UNIT 5
SAN CLEMENTE, CA 92672
(949) 637-3354
PREPARED BY:
PASCO LARET SUITER & ASSOCIATES, INC.
535 N. HIGHWAY 101, SUITE A
SOLANA BEACH, CA 92075
(858) 259-8212
Prepared: October 23, 2015
Revised: January 15, 2016
Revised: February 9, 2016
LER G. LAWSON, RCE 80356 DATE
PLSA 2276-02
I-03
TABLE OF CONTENTS
SECTION
Executive Summary 1.0
Introduction 1.1
Existing Conditions 1.2
Proposed Project 1.3
Conclusions 1.4
References 1.5
Methodology 2.0
Introduction 2.1
County of San Diego Criteria 2.2
Runoff Coefficient Determination 2.3
Hydrology & Hydraulic Model Output 3.0
Pre-Developed Hydrologic Calculations (100-Year Event) 3.1
Post-Developed Hydrologic Calculations (100-Year Event) 3.2
Appendix 4.0
Isopluvial Maps
Intensity Duration Design Charts
Runoff Coefficients
Overland Flow / Initial Time of Concentration
Hydrologic Soil Group - USDA Web Soil Survey
Pre-Development Hydrology Node Map
Post-Development Hydrology Node Map
PLSA 2276-02
1.0 EXECUTIVE SUMMARY
1.0 Introduction
This Preliminary Hydrology Study for the proposed development at 165 Chinquapin
Avenue has been prepared to analyze the hydrologic and hydraulic characteristics of the
existing and proposed project site. This report intends to present both the methodology
and the calculations used for determining the runoff from the project site in both the pre-
developed (existing) conditions and the post-developed (proposed) conditions produced
by the 2-year, 10-year, and 100-year, 6-hour storm.
1.1 Existing Conditions
The subject property is located along Chinquapin Avenue, west of the intersection of
Chinquapin Avenue and Garfield Street, in the City of Carlsbad. The site is bound by an
existing single family residential development to the west, an existing multi-family
residential development to the east of the property, Chinquapin Avenue to the north, and
the Agua Hedionda Lagoon to the south of the property. The existing site consists of an
existing residence, driveway, and associated improvements. The project site is located in
the Agua Hedionda Hydrologic Area, and, more specifically, the Los Monos Hydrologic
Sub-Area (904.31).
The existing site can be categorized into one drainage basin, and primarily drains from
the southeast to the northwest corner of the site and out to Chinquapin Avenue. An
existing asphaltic berm and sloping in the front yard along Chinquapin Avenue prevent
any offsite drainage from entering the parcel to the north. Existing residential properties
to the west and east prevent cross lot drainage from passing through the site. The
existing drainage basin has an approximate area of 0.23 acres and is approximately 46%
impervious. Per the Web Soil Survey application available through the United States
Department of Agriculture, the basin is generally categorized to have group B soils.
Based on the existing impervious area, a pre-development runoff coefficient of 0.55 was
calculated using the methodology described in section 3.1.2 of the San Diego County
Hydrology Manual and the formula provided therein. Using the Rational Method
Procedure outlined in the San Diego County Hydrology Manual, a peak flow rate and
time of concentration were calculated for a 100-year, 6-hour storm event. For the
existing drainage basin, the peak flow rate for the 100-year, 6-hour storm was determined
to be 0.83 cfs at the point of discharge from the site with a time of concentration of 5.0
minutes. Refer to pre-development hydrology calculations included in Section 3.1 of this
report for a detailed analysis of the existing drainage basin, as well as a pre-development
hydrology node map included in the appendix of this report for pre-development drainage
basin delineation and discharge locations.
1.2 Proposed Project
The proposed project includes the demolition of all existing onsite improvements and the
construction of a 3-unit detached condo map with associated private landscaping and
Page 1 of 8 PLSA 2276-02
hardscape improvements, as well as curb, gutter, and sidewalk improvements in the
public right-of-way. Site grading along with road, drainage and utility improvements
typical of residential developments will also be constructed. The proposed building pad
elevations range from 58.2 feet at the easterly unit to 56.6 feet at the westerly unit in an
attempt to match the existing sloping terrain.
In the resulting post-developed condition, runoff can be categorized into one drainage
basin similar to the existing site. Each unit will convey runoff by means of vegetated
swales to proposed area drains located along the southern and northern boundaries of the
property. Once water is collected in the area drains, PVC under drain pipes will
discharge the runoff into the proposed curb and gutter on Chinquapin Avenue.
The proposed drainage basin has an approximate area of 0.23 acres and is approximately
44% impervious. As in the existing condition, runoff is prevented from entering the site
due to proposed curb, gutter, sidewalk, and driveway improvements along Chinquapin
Avenue, and the neighboring residential developments to the west and east. Based on the
proposed impervious area, a runoff coefficient of 0.54 was calculated using the
methodology described in section 3.1.2 of the San Diego County Hydrology Manual and
the formula provided therein. Using the Rational Method Procedure outlined in the San
Diego County Hydrology Manual, a peak flow rate and time of concentration were
calculated for a 100-year, 6-hour storm event. For the proposed drainage basin, the peak
flow rate for the 100-year, 6-hour storm was determined to be 0.81 cfs at the ultimate
point of discharge with a time of concentration of 5.0 minutes. A storm drain curb inlet
located approximately 150 feet downstream west of the project at the low point of the
cul-de-sac on Chinquapin Avenue will then collect runoff from the curb and gutter and
direct it to the public storm drain system. Refer to post-development hydrology
calculations included in Section 3.2 of this report for detailed analysis of the proposed
drainage basin, as well as a post-development hydrology node map included in the
appendix of this report for post-development drainage delineation and discharge
locations.
In an effort to comply with the City of Carlsbad storm water standards, the proposed site
has incorporated LID design techniques to optimize the site layout. Runoff from
proposed roofs and hardscape areas will be directed to vegetated swales in an effort to
disperse drainage to pervious surfaces. The swales will remove sediment and particulate-
bound pollutants from storm water and will assist in decreasing peak runoff by slightly
increasing the site's overall time of concentration. Site hardscape has been minimized
with the addition of pervious paver walkways, driveways, and patios.
1.3 Conclusions
Based upon the analysis included in this report, there is a slight decrease in peak runoff as
a result of the proposed development, minimizing additional impacts to downstream
- properties and existing drainage facilities. Similar to the existing condition, the post-
developed site will discharge onto Chinquapin Avenue into the proposed curb and gutter
- system. Once in the gutter, drainage will be conveyed to an existing curb inlet located
Page 2 of 8 PLSA 2276-02
approximately 150 feet west of the project boundary, and will enter the buried pipe
network. Water will not be diverted away from existing drainage patterns, and the
decrease in proposed impervious area and resulting peak runoff will not have an adverse
effect on the downstream watershed. The post-developed site will be exempt from
hydromodification compliance requirements as it does not qualify as a Priority
Development Project as defined in the San Diego County Model BMP Design Manual.
Additional analysis and design will be required to verify that the proposed project is in
compliance with current stormwater quality regulations.
1.5 References
"San Diego County Hydrology Manual ", revised June 2003, County of San Diego,
Department of Public Works, Flood Control Section.
"San Diego County Hydraulic Design Manual", revised October 2012, County of San
Diego, Department of Public Works, Flood Control Section
"Model BMP Design Manual San Diego Region ", adopted June 27, 2015, San Diego
Region
"Low Impact Development Handbook - Stormwater Management Strategies", revised
July 2014, County of San Diego, Department of Public Works
Soil Survey Staff, Natural Resources Conservation Service, United States Department of
Agriculture. Web Soil Survey. Available online at http://websoilsurvey.nrcs.usda.gov.
Accessed July 20, 2015
Page 3 of 8 PLSA 2276-02
2.0 METHODOLOGY
2.1 Introduction
The hydrologic model used to perform the hydrologic analysis presented in this report
utilizes the Rational Method (RM) equation, Q--CIA. The RM formula estimates the
peak rate of runoff based on the variables of area, runoff coefficient, and rainfall
intensity. The rainfall intensity (I) is equal to:
I = 7.44 x P6 x D 045
-. Where:
I = Intensity (in/hr)
P6 = 6-hour precipitation (inches)
D = duration (minutes - use Tc)
Using the Time of Concentration (Tc), which is the time required for a given element of
water that originates at the most remote point of the basin being analyzed to reach the
point at which the runoff from the basin is being analyzed. The RM equation determines
the storm water runoff rate (Q) for a given basin in terms of flow (typically in cubic feet
per second (cfs) but sometimes as gallons per minute (gpm)). The RM equation is as
follows:
Q=CIA
VAJ T,473
Q= flow (in cfs)
C = runoff coefficient, ratio of rainfall that produces storm water
runoff (runoff vs. infiltration/evaporation/absorption/etc)
I = average rainfall intensity for a duration equal to the Tc for the
area, in inches per hour.
A = drainage area contributing to the basin in acres.
The RM equation assumes that the storm event being analyzed delivers precipitation to
the entire basin uniformly, and therefore the peak discharge rate will occur when a
raindrop that falls at the most remote portion of the basin arrives at the point of analysis.
The RM also assumes that the fraction of rainfall that becomes runoff or the runoff
coefficient C is not affected by the storm intensity, I, or the precipitation zone number.
Page 4 of 8 PLSA 2276-02
2.2 County of San Diego Criteria
As defined by the County Hydrology Manual dated June 2003, the rational method is the
preferred equation for determining the hydrologic characteristics of basins up to
approximately one square mile in size. The County of San Diego has developed its own
tables, nomographs, and methodologies for analyzing storm water runoff for areas within
the county. The County has also developed precipitation isopluvial contour maps that
show even lines of rainfall anticipated from a given storm event (i.e. 100-year, 6-hour
storm).
One of the variables of the RM equation is the runoff coefficient, C. The runoff
- coefficient is dependent only upon land use and soil type and the County of San Diego
has developed a table of Runoff Coefficients for Urban Areas to be applied to basin
located within the County of San Diego. The table categorizes the land use, the
associated development density (dwelling units per acre) and the percentage of
-
impervious area. Each of the categories listed has an associated runoff coefficient, C, for
each soil type class.
The County has also illustrated in detail the methodology for determining the time of
concentration, in particular the initial time of concentration. The County has adopted the
Federal Aviation Agency's (FAA) overland time of flow equation. This equation
essentially limits the flow path length for the initial time of concentration to lengths under
- 100 feet, and is dependent on land use and slope. The time of concentration minimum is
5 minutes per the County of San Diego requirements.
2.3 Runoff Coefficient Determination
As stated in section 2.2, the runoff coefficient is dependent only upon land use and soil
type and the County of San Diego has developed a table of Runoff Coefficients for Urban
Areas to be applied to basin located within the County of San Diego. The table, included
at the end of this section, categorizes the land use, the associated development density
(dwelling units per acre) and the percentage of impervious area.
Page 5 of 8 PLSA 2276-02
3.0 HYDROLOGY MODEL OUTPUT
3.1 Pre-Developed Hydrologic Model Output (100-Year Event)
Pre-Development:
Q=CIA
P2=1.2
P101.7
- P1002.5
Basin 1
Total Area = 9,972 sf 4 0.229 Acres
Impervious Area = 4,586 sf 4 0.11 Acres
Pervious Area = 5,386 sf 4 0.12 Acres
Cn, Weighted Runoff Coefficient
- 0.25, Cn value for natural ground, Type B soils
* Per San Diego Hydrology Design Manual (SDHDM) Section 3.1.2
- 0.9, C value for developed / impervious surface
* Per SDHDM Section 3.1.2
Cn = 0.9 x 4,586 sf+ 0.25 x 5,386 sf= 0.55
9,972 sf
Tc =.5.0 Mm (minimum for small areas)
P6 = 2.5
I = 7.44 x P6 D 045
I = 7.44 x 2.5 x 6.59
Iwo 6.59 in/hr
1 I23.16 in/hr
Iio 4.48 in/hr
Q2 = 0.55 x 3.16 in/hr x 0.229 Ac = 0.40 cfs
Qio = 0.55 x 4.48 in/hr x 0.229 Ac = 0.56 cfs
- Qioo = 0.55 x 6.59 in/hr x 0.229 Ac = 0.83 cfs
Page 6 of 8 PLSA 2276-02
3.2 Post-Developed Hydrologic Model Output (100-Year Event)
Post-Development (without considerin2 HMP/BMP treatment):
Q=CIA
P2=1.2
P10=1.7
P100=2.5
Basin A
Total Area = 9,972 sf 4 0.229 Acres
Impervious Area = 4,376 sf4 0.10 Acres
Pervious Area = 5,595 sf4 0.13 Acres
Cn, Weighted Runoff Coefficient
- 0.25, Cn value for natural ground, Type B soils
* Per San Diego Hydrology Design Manual (SDHDM) Section 3.1.2
- 0.9, C value for developed / impervious surface
* Per SDHDM Section 3.1.2
- Cn = 0.9 x 4,376 sf+ 0.25 x 5,595 sf= 0.54
9,972 sf
Tc =.5.0 Mm (mm. for small areas)
P6 = 2.5
I = 7.44 x P6 D.0645
I = 7.44 x 2.5 x s.O-° 6.59 in/hr
Iioo 6.59 in/hr
I2 3.16 in/hr
Iio 4.48 in/hr
*At northwest corner under drain
Ai = 7,779 sf 4 0.18 Acres
Q2 = 0.54 x 3.16 in/hr x 0.18 Ac = 0.31 cfs
Qio = 0.54 x 4.48 in/hr x 0.18 Ac = 0.44 cfs
Qioo = 0.54 x 6.59 in/hr x 0.18 Ac = 0.64 cfs
Page 7 of 8 PLSA 2276-02
*At sidewalk under drain
A2 = 1,080 sf 4 0.02 Acres
Q2 = 0.54 x 3.16 in/hr x 0.025 Ac = 0.04 cfs
Qio = 0.54 x 4.48 in/hr x 0.025 Ac = 0.06 cfs
Qioo = 0.54 x 6.59 in/hr x 0.025 Ac = 0.08 cfs
*At sidewalk under drain
A.3 = 1,102 sf 4 0.03 Acres
Q2 = 0.54 x 3.16 in/hr x 0.03 Ac = 0.05 cfs
Qio = 0.54 x 4.48 in/hr x 0.03 Ac = 0.07 cfs
Qioo = 0.54 x 6.59 in/hr x 0.03 Ac = 0.09 cfs
*Total leaving site at ultimate discharge point
Qioo = 0.54 x 6.59 in/hr x 0.229 Ac = 0.81 cfs
Pre-Development vs. Post-Development (Discharge Leaving Site):
Pre-Development Post-Development Delta
Qioo = 0.83 cfs Qioo = 0.81 cfs -0.02 cfs
Page 8 of 8 PLSA 2276-02
4.0 APPENDIX
PLSA 2276-02
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San Diego County Hydrology Manual Section: 3
Date: June 2003 - Page: 6 of 26
Table 3-1
RUNOFF COEFFICIENTS FOR URBAN AREAS
Land Use Runoff Coefficient "C"
Soil Type
NRCS Elements County Elements % IMPER. A B C D
Undisturbed Natural Terrain (Natural) Permanent Open Space 0* 0.20 0.25 0.30 0.35
Low Density Residential (LDR) Residential, 1.0 DU/A or less 10 0.27 0.32 0.36 0.41
Low Density Residential (LDR) Residential, 2.0 DU/A or less 20 0.34 0.38 0.42 0.46
Low Density Residential (LDR) Residential, 2.9 DU/A or less 25 0.38 0.41 0.45 0.49
Medium Density Residential (MDR) Residential, 4.3 DU/A or less 30 0.41 0.45 0.48 0.52
Medium Density Residential (MDR) Residential, 7.3 DU/A or less 40 0.48 0.51 0.54 0.57
Medium Density Residential (MDR) Residential, 10.9 DU/A or less 45 0.52 0.54 0.57 0.60
Medium Density Residential (MDR) Residential, 14.5 DU/A or less 50 0.55 0.58 0.60 0.63
High Density Residential (HDR) Residential, 24.0 DU/A or less 65 0.66 0.67 0.69 0.71
High Density Residential (FLDR) Residential, 43.0 DU/A or less 80 0.76 0.77 0.78 0.79
Commercial/Industrial (N. Corn) Neighborhood Commercial 80 0.76 0.77 0.78 0.79
Commercial/Industrial (G. Com) General Commercial 85 0.80 0.80 0.81 0.82
Commercial/Industrial (O.P. Corn) Office Professional/Commercial 90 0.83 0.84 0.84 0.85
Commercial/Industrial (Limited I.) Limited Industrial 90 0.83 0.84 0.84 0.85
Commercial/Industrial (General 1.) General Industrial 95 0.87 0.87 0.87 0.87
*The values associated with 0% impervious may be used for direct calculation of the runoff coefficient as described in Section 3.1.2 (representing the pervious runoff
coefficient, Cp, for the soil type), or for areas that will remain undisturbed in perpetuity. Justification must be given that the area will remain natural forever (e.g., the area
is located in Cleveland National Forest).
DU/A = dwelling units per acre
NRCS = National Resources Conservation Service
3-6
San Diego County Hydrology Manual Section: 3
Date: June 2003 Page: I2of26
Note that the Initial Time of Concentration should be reflective of the general land-use at the
upstream end of a drainage basin. A single lot with an area of two or less acres does not have
a significant effect where the drainage basin area is 20 to 600 acres.
Table 3-2 provides limits of the length (Maximum Length (LM)) of sheet flow to be used in
hydrology studies. Initial Ti values based on average C values for the Land Use Element are
also included. These values can be used in planning and design applications as described
below. Exceptions may be approved by the "Regulating Agency" when submitted with a
detailed study.
Table 3-2
MAXIMUM OVERLAND FLOW LENGTH (LM) -'
& INITIAL TIME OF CONCENTRATION (T
Element* DU/
Acre
.5% 1% 2% 3% 5% 10%
LM T1 LM T1 LM Tj LM T1 LM T, LM Ii
Natural 50 13.2 70 12.5 85 10.9 100 10.3 100 8.7 100 6.9
LDR 1 50 12.2 70 11.5 1 85 10.0 100 9.5 100 8.0 1 100 6.4
LDR 2 50 11.3 70 10.5 85 1 9.2 100 8.8 100 7.41 100 1 5.8
LDR 2.9 50 1 10.7 70 10.0 85 8.8 95 8.1 100 7.0 100 5.6
MDR 4.3 50 10.2 70 9.6 80 8.1 95 7.8 100 6.7 100 5.3
MDR 7.3 50 9.2 65 1 8.41 80 7.4 95 7.0 100 6.0 100 4.8
MDR 10.9 50 8.7 65 7.91 801 6.9 90 6.4 100 5.71 100 4.5
MDR 14.5 50 8.2 65 7.41 80 6.5 1 90 6.0 100 5.4 100 4.3
HDR 124 50 1 6.7 65 6.1 75 5.1 90 4.9 95 4.3 100 3.5
HDR 43 50 5.3 65 4.7 75 4.0 85 3.8 1 95 3.4 100 2.7
N. Corn 50 5.3 60 4.5 75 4.0 85 3.8 95 3.4 100 2.7
G. Corn 50 4.7 60 4.1 1 75 3.6 85 3.4 90 2.9 100 2.4
O.P./Corn 50 4.2 60 3.7 70 3.1 80 2.9 90 2.6 100 2.2
Limited 1. 50 4.2 60 3.7 70 3.1 80 2.9 90 1 2.6 1 100 2.2
General I. 50 3.7 60 3.2 70 2.7 80 2.6 90 2.3 100 1.9
*See Table 3-1 for more detailed description
3-12
Hydrologic Soil Group—San Diego County Area, California
33 851"N
%.
Hydrologic Soil Group—San Diego County Area, California
Hydrologic Soil Group
Hydrologic Siil Group— Summary by Map Unit - San Diego County Area, California (CA38)
Map unit symbol,,Map unit name Rating Acres In AOl Percent of AOl
MIC Marina loamy coarse
sand, 2 to percent
slopes
B 1.8 82.1%
TeF Terrace escarpments 0.4 17.9%
Totals for Area of Interest 2.2 100.0%
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 (AID, BID, and CID). 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 (AID, BID, 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.
Rating Options
Aggregation Method: Dominant Condition
usn Natural Resources Web Soil Survey 10/21/2015
Conservation Service National Cooperative Soil Survey Page 3 of 4
Hydrologic Soil Group—San Diego County Area, California
Component Percent Cutoff. None Specified
Tie-break Rule: Higher
usn Natural Resources Web Soil Survey 10/21/2015
Conservation Service National Cooperative Soil Survey Page 4 of 4
Tuesday, Jan 12 2016
Highlighted
Depth (ft) = 0.25
Q(cfs) = 0.125
Area (sqft) = 0.05
Velocity (ft/s) = 2.54
Wetted Perim (ft) = 0.79
Crit Depth, Yc (ft) = 0.22
Top Width (ft) = 0.00
EGL(ft) = 0.35
0 1
Elev (ft)
55.00
54.75
54.25
54.00
Channel Report
Hydraflow Express Extension for Autodeslø8) AutoCAD® CiI 3D® by Autodesk, Inc.
3-in PVC Drain Pipe @ 2% (QIOO)
Circular
Diameter (ft) = 0.25
Invert Elev (ft) = 54.60
Slope (%) = 2.00
N-Value = 0.013
Calculations
Compute by: Known Depth
Known Depth (ft) = 0.25
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