HomeMy WebLinkAboutTR 35337 HYDROLOGY REPORT-001 HYDROLOGY STUDY
['OR
TRACT 35337
CITY Ol' LAIxE ELSINORE
1- ITXIT OH' C:AI ,l F'OlZN l A
VOLUME 1
REPORT
PREPARED FOR:
SPYGLASS RANCH (RIVERSIDE), ASLI V, LLLP
CIO PACIFIC COVES IN\ESTMENTS, LLC
23 BALBOA COVES
NEWPORT BEACH, CA 92663
PREPARED BY:
a 1
Engineering, Inc.
357 N. SHERIDAN STREET, SUITE 117
CORONA, CA 92880
PHONE: (951) 279 1800
FAX: (951) 279 4380
March 2013
PREPARED UNDER THE SUPERVISION OF:
FARRIS N. HADDAD RCE NO. 65931 DATE
Spyglasq Ranch Tract 35337
Hydrology Report
TABLE OF CONTENTS FOR VOLUME 1
Report
General Project I
Figure 1: Vicinity Map 1
Figure 2: Site and Development Stages 2
Design Criteria 3
Scope of Report 3
Methodology 4
Pre-Developed Condition 5
Table 1: Existing Culvert Drainage Areas 6
Post-Developed Condition 7
Figure 3: Onsite Basins 9
Results and Summary
Table 2: Rational Method Summary - Stage 1 10
Figure 4: Stage 1...Area Balance 11
Table 3: Rational Method Summary - Ultimate 11
Figure 5: Ultimate...Area Balance 12
Area "A" and Basin #2 13
Table 4: Basin #2 - Volume vs. Depth 13
Table 5: Basin #2 - Volume vs. Depth for WQ 14
Table 6: Basin #2 - Depth vs. Outflow 15
Table 7: Basin #2 Outlet Structure...Summary 16
Table 8: Basin #2 Detention...Route Summary 16
Table 9: Post-Developed Q...to Existing RCB Culvert 17
Area "B" 17
Area "C" (JDA Area) 17
Figure 6: Developed Areas Tributary to Tract 31593 18
Area "D" and Basin #3 19
Table 10: Unit Hydrograph Summary - 10-year Study 19
Table 11: Basin #3 - Volume vs. Depth 20
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Spyglass Ranch Tract 35337
Hydrology Report
Results and Summary (continued)
Table 12: Basin #3 - Volume vs. Depth for WQ 20
Table 13: Basin #3 - Depth vs. Outflow 21
Table 14: Basin #3 Outlet Structure...Summary 22
Table 15: Basin #3 Detention...Route Summary 23
Table 16: Basin #1 - Volume vs. Depth for WQ 24
Area "E" and Basin #1 23
Area "F" and "G" 24
Area "H" 24
Area "I" 25
Area "J" 25
Area "K" 25
Area "L" (JDA Area) 26
Area "M" 26
Basin Spillways and Auxiliary Outlets 27
Conclusion 27
Hydrology Maps
• Existing Condition Hydrology Map
• Developed Condition Hydrology Map, Stage 1 Condition
• Developed Condition Hydrology Map, Ultimate Condition
Exhibits
A. Unit Hydrograph Exhibits
• Existing Condition Unit Hydrograph Area 9
• Developed Condition Unit Hydrograph Area "A"
• Developed Condition Unit Hydrograph Area '°D" Stage 1
• Developed Condition Unit Hydrograph Area I°D" Stage 1 Tributary
to Basin #3
B. Street Capacity Tables
C. Catch Basin Summary Table
D. Node Model Data Flow Sheets (Rational Method)
• Existing Condition
• Stage 1 Condition
• Ultimate Condition
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Spyglasq Ranch Tract 35337
Hydrology Report
TABLE OF CONTENTS FOR VOLUME 2 (COMPUTER DISK)
Appendix — Computation Output Files
A. Rational Method
• Existing Rational 100—Year Storm
• Developed Rational 10—Year Storm Stage 1
• Developed Rational 100—Year Storm Stage 1
• Developed Rational 10—Year Storm Ultimate (Areas C, D, and Q
• Developed Rational 100—Year Storm Ultimate (Areas C, D, and Q
B. Unit Hydrograph Method
• Existing Unit Hydrograph Area 9 (10—Year Storm, 6 and 24 hour
durations)
• Developed Unit Hydrograph Area "A" (100—Year Storm, 1 hour
duration)
• Developed Unit Hydrograph Area "D" Stage 1 (10—Year Storm, 6
and 24 hour durations)
• Developed Unit Hydrograph Area "D" Stage 1 Tributary to Basin
#3 (10—Year Storm, 6 and 24 hour durations)
C. Basin Routing
• Storm Mitigation for Basin #2
• Storm Mitigation for Basin #3
• Water Quality for Basin #2
• Water Quality for Basin #3
• Spillways for Basins #1, #2, and #3
D. Catch Basins (10—Year and 100—Year Storm Frequencies)
• Area A
• Area C
• Area D
• Area E
• Camino Del Norte
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Spyglass Ranch Tract 35337
Hydrology Study
Report
General Project —
Tract 35337, also known as "Spyglass Ranch," is a proposed development
located in the City of Lake Elsinore, Riverside County, California (see Figure
1). The project is a master—planned community that consists of
approximately 260 acres of mixed landuse implemented in accordance with
the Spyglass Ranch Specific Plan No. 2005-02.
4 J�x
Project
!� L
Site
r.
LVE
JN1i�R //
E)YAOPE \
Figure 1: Vicinity Map
No Scale
The development includes about 444 single family lots, eight acres
dedicated to estate residential lots, courtyard units, multi—family units with
an optional commercial site, and a six—acre public park. The project takes
its primary access from Camino Del Norte, north and south of Main Street.
The secondary access is from Elsinore Hills Road, which is proposed to
extend to the north through Tract 31593 and connect to the existing road
terminus within the Ramsgate Community in Tract 25478.
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Spyglass Ranch Tract 35337
Hydrology Study
The project is to be constructed in two stages with the majority of the
development graded in Stage 1. The first stage of development is mostly
independent and does not require facilities from other projects to be
constructed in order to proceed. The second and final stage of the project
may require such implementing facilities and likely will only occur
concurrent with or after Tract 31593 is constructed (see Figure 2).
EICHORN PROPERTY TRACT 31593
PM 985 I�
TRACT 35337 "SPYGLASS RANCH" iSTAGE 2 0
co
co
Cl� S TAG E 1 H
H
CD
Figure 2: Site and Development Stages
No Scale
Spyglass Ranch also supports a new water reservoir on site to serve the
1801 water pressure zone. Although the tank site is located within the
second stage of grading, it must be constructed with the first stage of
grading since a large number of lots will be served by it. The reservoir
will also be used to support the development within Tract 31593.
Because of the phased grading, the required reservoir site, and the
unknown construction timing of Tract 31593, interim condition drainage
patterns may be created at the time of construction of Spyglass Ranch.
Consequently, the different scenarios that impact the hydrology of the site
are addressed, analyzed, and compared in this report.
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Spyglass Ranch Tract 35337
Hydrology Study
— Design Criteria —
The Spyglass Ranch project is conditioned by the City of Lake Elsinore
to provide a drainage study to identify storm water runoff, to show existing
and proposed onsite and offsite drainage facilities, and to provide the
proper capacity analyses to verify the adequacy of the proposed drainage
improvements. Natural drainage courses traversing the site must be
conveyed through the site, or should be collected and conveyed in such a
manner that is approved by the City Engineer. All offsite drainage, if
different from historic drainage patterns, shall be conveyed to a public
facility, or accepted by an adjacent property owner by a letter of drainage
acceptance, or conveyed to a drainage facility within an easement.
Furthermore, the drainage system shall be designed to ensure that
runoff from a 10—year storm event of 6 hour or of 24 hour durations
under the developed condition is equal to or less than the runoff under
the existing conditions of the same storm frequency. Both the 6 hour and
the 24 hour storm durations shall be analyzed to determine the onsite
detention basin capacities necessary to accomplish the desired results.
Onsite peak flow rates for the 10—year storm event are to be managed
at or below the curb line; peak flow rates for the 100—year storm event
are to be managed within the right—of—way (R/W) limits. If these limits
are exceeded, underground storm drain facilities must be provided to lower
the water surface levels in the roadway to or below the maximum indicated
levels.
Water quality treatment and conveyance is to be provided in accordance
with NPDES requirements to be implemented per the Regional Water Quality
Control Board standards and guidelines for the Santa Ana Watershed. The
required water quality treatment volumes and basin capacities are
determined per the City's WQMP handbook (worksheets included in this
report) and are to be consistent with the approved Spyglass Ranch
Preliminary WQMP. Water quality basins must provide an outlet designed to
retain a minimum of half of the water quality design volume for a
minimum of 24 hours and the remaining water quality design volume for a
minimum of 48 hours, but no longer than 72 hours.
Overall, the project site must be designed to safely convey the 100—Year
storm event through the site should failure of the underground storm drain
system occur. Any further criteria for this report is provided by and
based on the RCFCWCD hydrology manual.
— Scope of Report —
The purpose of this study is to calculate the storm water runoff
associated with the proposed development as necessary to satisfy the City's
conditions and requirements for the drainage study. Results from this
study will be used to (1) provide the design flow rates that the storm
drain system is designed to manage, and (2) analyze the increase runoff
due to development and determine the amount of mitigation where
necessary. The results from this study will be used to size and/or confirm
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Spyglass Ranch Tract 35337
Hydrology Study
the storm drain pipes, catch basins, onsite detention basin volumes and
hydraulic performance, detention basin outflow structures (water quality
control and storm mitigation), and the street flood capacity. This study
considers the conveyance of all the local onsite and tributary offsite
drainage flows for both the ultimate and interim conditions.
This study includes the hydraulic analysis and design of the culvert
system being used in the post—developed condition that is located along
the project frontage on Camino Del Norte. The proposed development is
considered to have no adverse hydraulic impacts on the downstream
conveyance facilities located along the westerly side of the Freeway that
drain northerly. Consequently, analysis of these downstream facilities is
not necessary and is therefore excluded from this study.
The study includes a general evaluation of the Wasson Canyon Basin, a
Municipal Separate Storm Sewer System ("MS4") facility, which is located
downstream and approximately 800 feet from the project's westerly
boundary. The Basin is owned and operated by the Riverside County Flood
Control District (RCFCD) and is to serve as an ultimate discharge point for
a large part of the project's drainage runoff. The purpose of the
evaluation is to confirm that the Basin is not adversely impacted by the
proposed development flows. The Basin Plan referenced in this study is
the Wasson Canyon Channel Stage I RCFCD Project No. 3-0-180.
— Methodology —
Rational method hydrology is implemented to calculate the 100—year and
10—year storm frequency peak flow rates. Drainage areas are determined
and defined using ridgeline boundaries and "link—node" streams. The
rational calculations are performed by Rational Method Riverside County
("RRIV") provided in the Civil Design Software suite, developed by Joseph E.
Bondiman & Associates and recommended by RCFCWCD. Rainfall, loss rates,
and other such data that is pertinent to the rational method calculations
are determined by "RRIV" and summarized within the output files provided
herein. By combining the "link—node" rational method in the 'RRIV"
program with street depth and catch basin capture calculations, the storm
drain pipes and catch basin sizes are determined. These values dictate
the placement and sizing of the underground drainage facilities based upon
the street capacity. This method makes use of "RRIV" for primarily three
values: peak flow rates, time of concentration, and accumulated drainage
area. Values generated by "RRIV" that are neglected and may be found
more accurately, as determined in the hydraulic calculations, include depth
of street flow, street capacity calculations, and catch basin capture
calculations.
Synthetic unit hydrograph modeling is used in accordance with City and
RCFCWCD requirements and guidelines to study the appropriate storm return
frequencies and durations to be mitigated. Mitigation for the necessary
conditions will be achieved thorough detention basins and the use of a
control outlet valve structure. The software employed to compute the unit
hydrographs and basin routing calculations are contained within the Civil
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Spyglass Ranch Tract 35337
Hydrology Study
Design Software suite and recommended by RCFCWCD. Rainfall, loss rates,
AMC requirements, and other such data that is pertinent to the
development of the unit hydrographs are based upon Increased Runoff
Criteria typically required by RCFCWCD.
— Pre—Developed Condition —
By in large, the soil type for the majority of this site has a high runoff
potential, as designated by the U.S. Soils Conservation Service (SCS) as Soil
Groups C and D. These areas are characterized as having a low capacity
to transmit water, thereby resulting in a slow to very slow rate of
infiltration, and a relatively high volume of runoff. There are, however,
some minor areas that are characterized as having moderate infiltration
rates, designated as SCS Soil Group B (ref. RCFCD Hydrology Manual Plate
C-1.41). The appropriate ratio of each soil group is used in the existing
condition model of this study. Another factor that adds to the high
potential for storm runoff due to the existing soil type is that the site
also has poor ground cover. For purposes of these study computations,
poor soil cover is basically defined by SCS as a watershed having less than
fifty—percent of its ground surface covered by tree canopy and brush.
Another factor that will generate a high rate of runoff in the existing
condition is the significant relief across the site. Generally, the lay of the
land flows in a south to southwesterly direction towards Lake Elsinore,
which sits just over one mile downstream of the subject tract. The highest
elevation within the site is approximately 1800 feet MSL and the lowest
elevation is approximately 1300 feet MSL. The existing terrain is
mountainous with significant hill and valley formations. Storm runoff from
the site takes several different local paths from the project site prior to
reaching the Lake, the ultimate discharge point. A number of ridgelines
divide the site into distinct drainage areas that create flow paths in all
directions. Because of this, there are many drainage courses that outlet
across the boundary on all sides of the project.
Yet, since the site is relatively elevated within its vicinity, there are
essentially no substantial offsite flows that are tributary to the site.
Generally speaking, the site's watershed boundary nearly matches the
project boundary with flow patterns that run from onsite to offsite.
However, there are three areas that contain a drainage course that has
multiple project boundary crossings, flowing offsite to onsite and vice versa.
Referencing the Existing Condition Hydrology Map, these areas are identified
as Areas 2, 4, and 12. These drainage areas do not raise a great deal of
concern since the offsite contribution within these sub—areas is relatively
minimal. These drainage areas are discussed further in their post—
developed condition under the following section of this report.
Although the majority of the drainage areas are treated in a standard
manner as they relate to the existing and developed conditions, there are
three edge conditions that are worthy to note. The first is the frontage
along Camino Del Norte, the second is the far west boundary that is
adjacent to Parcel Map (PM) 30985, and the third is the north boundary
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Spyglass Ranch Tract 35337
Hydrology Study
that is adjacent to Tract 31593, also referred to herein as "South Shore."
Each of these areas will be addressed throughout the report as they relate
to the post—developed conditions under the ultimate condition, interim
condition, or both scenarios when applicable. Following is a brief
description of these three edge conditions in their existing states.
Firstly, to the southwest, there are five identifiable drainage areas that
are intercepted by existing culverts located along the frontage road, Camino
Del Norte. The series of culverts along Camino Del Norte are maintained
by the City and are designed to capture flows generated from the site,
then convey them under the I-15 Freeway, then along the westerly side of
the I-15 Freeway towards the Wasson Canyon Basin, and then into the Lake
Elsinore Channel. The areas tributary to the existing culverts are
identified in the Existing Condition Hydrology Map as Areas 12 through 16,
inclusive. Table 1 lists each drainage area and the culvert it discharges
into.
Table 1: Existing Culvert Drainage Areas
Drainage Area Designation Existing Culvert Description Node
12 54" CSP 1213
13 36" ACP 1.301
18" AC P
14 30" ACP 1403
15 18" CSP 1502
16 30" ACP 1603
Notes:
1. Node numbers reference the Existing Condition Hydrology Map.
The 54" culvert inlet is a concrete headwall structure located at an
existing drainage course near an existing access road. The other smaller
culvert inlets are grated inlets generally located along the toe of slope at
the project's frontage that are designed to intercept runoff from the site
that drains off of the road slopes. The 36" and 18" culverts designated as
nodes 1305 and 1308, respectively, confluence just downstream of their
inlets at node 1.031, as reflected in Table 1.
Secondly, there is an existing 61x5' RCB culvert located in Camino Del
Norte approximately 700 feet northerly of the Spyglass Ranch west project
boundary. The inlet to the RCB is a concrete headwall structure that is
located at the frontage of the downstream property, PM 30985, and is
maintained by the City. This RCB culvert extends beneath Camino Del
Norte and the I-15 Freeway and connects to a 54" reinforced concrete pipe
(RCP) near the Wasson Canyon Channel at Collier Avenue, just upstream of
the Wasson Canyon Basin. PM 30985 indicates an approved design flow rate
for the RCB culvert of 168 cfs at the inlet within its property, and 185 cfs
downstream of the two minor catch basin lateral connections that occur in
Camino Del Norte just downstream of the inlet. The majority of this flow
is generated by an existing drainage course that enters PM 30985 from its
east boundary through the Spyglass Ranch property. The drainage area
within Spyglass Ranch that is tributary to this drainage course is identified
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Spyglass Ranch Tract 35337
Hydrology Study hI ^
LJ
as Area 2. PM 30985 shows that it accepts an approved flow rate from
Spyglass Ranch at their common boundary of 128 cfs. This runoff is
depicted per the PM 30985 improvement plans to be intercepted in a 71x3'
RCB headwall inlet structure that is located at the common property line.
Thirdly, there is a drainage area whose drainage course crosses at
multiple locations the portion of the north boundary adjacent to the South
Shore development. The area tributary to this drainage course is identified
as Area 4. It can be observed that the primary drainage course in Area 4
originates within Spyglass Ranch (at node 401), then crosses the north
boundary into South Shore (at node 402), then re-enters Spyglass Ranch
(near node 403), and finally crosses the north boundary a third time into
South Shore (at node 406) before confluencing with another drainage course
(at node 407) within the South Shore property that drains westerly. It is
noteworthy that a special condition is presented by this drainage area that
will be further addressed under the Post-Developed Section of this report.
Post-Developed Condition -
Stage 1 and Ultimate Condition Scenarios
This study takes under consideration two different construction scenarios
for the Spyglass Ranch development. Spyglass Ranch is proposed to be
graded in two stages, as depicted in Figure 2. Stage 1 is comprised of the
first five of the seven tract phases (i.e. 35337-1, -2, -3, -4, and -5) and
includes the vast majority of the single family residential lots along with
the park site and the higher-density development parcels. Since
construction of Stage 1 can be completed mostly independent of South
Shore commencing work, there is an interim condition construction scenario
that is plausible, and thus used as one of the two overall post-developed
models evaluated in this study. This interim condition occurs after the
Stage 1 grading is complete and South Shore is not yet constructed. At
this stage, there is significant offsite grading that is necessary for Spyglass
Ranch in order to complete the road and lot construction in the vicinity of
its common boundary with South Shore. This condition is called "Stage 1"
for purposes of this report. It is noteworthy that Stage 1 also includes the
construction of the water tank site and the appropriate access road to it.
The "Developed Condition Hydrology Map - Stage 1" depicts this lot
configuration and grading scenario.
Stage 2 is comprised of the last two of the seven tract phases (i.e.
35337-6, -F) that includes single family residential lots and several larger
estate residential lots. Since construction of Stage 2 is dependent on South
Shore for access, it is plausible that Stage 2 will be constructed either
concurrent with or after South Shore develops. Thus, the Stage 2 grading
scenario is evaluated under the ultimate (i.e. built out) condition for both
projects and used as the second of the two overall post-developed models
evaluated in this study. This condition occurs after the Stage 2 grading is
complete and South Shore is constructed in its entirety. At this stage,
secondary access is available for the Spyglass Ranch final phases at its
common boundary with South Shore. This condition is called "Ultimate" for
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Spyglass Ranch Tract 35337
Hydrology Study
purposes of this report. It is noteworthy that the ultimate condition does
not consider any interim offsite grading into the South Shore project. The
"Developed Condition Hydrology Map - Ultimate Condition" depicts this lot
configuration and grading scenario.
It is important to note that three of the thirteen developed drainage
areas presented in this study are impacted differently under each of the
Stage 1 and Ultimate scenarios. Accordingly, two sets of computations are
provided for the rational analysis for these three areas - one for the
Stage 1 condition and the other for the Ultimate condition. The other ten
drainage areas are essentially the same under either scenario.
Basins
Spyglass Ranch supports three drainage basins that serve as either
water quality basins, storm mitigation facilities, or both. See "Figure 3:
Onsite Basins." The basins are designed to be in compliance with RCFCD
standards and guidelines and are briefly described below. Detail basin
routing computations and water quality design worksheets can be found in
the Appendix of this report and in the Spyglass Ranch Water Quality
Management Plan (WQMP).
Basin #1 is an off-line, single purpose water quality infiltration
basin. The primary basin area plus the forebay area have an overall
volume capacity of about 100,600 cubic feet, or 2.3 acre-feet. The basin is
designed to treat about 53 acres of development. A bifurcation structure
at the storm drain main line will divert only the required water quality
volume from the main line and into the basin. Storm flows are designed
to bypass the basin and discharge directly into the existing culvert located
in Camino Del Norte. A relief underdrain and emergency overspill
structure is provided for the basin in case of minor storm flow escape into
the basin from the mainline and in case of infiltration failure.
Basin #2 is an in-line, dual purpose extended detention basin. The
primary basin area plus the forebay area have an overall volume capacity
of about 252,000 cubic feet, or 5.8 acre-feet. The basin is designed to
mitigate and treat about 69 acres of development. All tributary storm flows
from the storm drain system will be discharged into the basin. The basin
is designed to treat the first flush flows for water quality and mitigate the
higher storm flows with the use of a control basin outlet valve. The basin
outlet pipe located in Camino Del Norte will connect and discharge the
mitigated flows into the existing RCB culvert located about 700 feet
downstream of the basin. The basin is designed to mitigate the higher
storm flows such that the total post-developed flow rate generated from
Spyglass Ranch that enters the existing RCB culvert does not exceed the
approved flow rate in the existing RCB culvert. An emergency overspill
structure is provided for the basin in case of an outlet structure failure.
Basin #3 is an in-line, dual purpose extended detention basin. The
primary basin area plus the forebay area have an overall volume capacity
of about 103,000 cubic feet, or 2.4 acre-feet. The basin is designed to
mitigate and treat 28 acres of development. All tributary storm flows from
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Spyglass Ranch Tract 35337
Hydrology Study
o
Basin #2
Basin #3
Basin #1
Figure 3: Onsite Basins
No Scale
the storm drain system are designed to discharge into the basin. The
basin is designed to treat the first flush flows for water quality and
mitigate the higher storm flows with the use of a control basin outlet
valve. The basin outlet pipe will discharge the mitigated storm flows into
the existing drainage course on the adjacent downstream property. An
emergency overspill structure is provided for the basin in case of an outlet
structure failure.
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Spyglass Ranch Tract 35337
Hydrology Study A
Table 3: Rational Method Summary - Ultimate Condition Variable Areas
D.18 & D.19 6, 7, 8 9.7 20.9 4.11 6.60
L 5 50.0 31.0 18.09 10.55
Sub-Total: 94.46 100.52
Similar Total Areas from Table 1: 200.22 193.32
Totals: 294.68 293.84
Notes:
1. Existing point assumed at Node 407 for purposes of comparison.
2. Developed Q shown for purposes of comparison equals summation of Q at
Nodes 0.305, 0.306, 334.1, 336.1, 346, and 347.1.
It may be observed that there is a slight difference between the total
developed condition drainage area and the total existing condition drainage
area (i.e. 294.76 vs. 293.84 acres). The minor difference is attributed
primarily to the proposed offsite grading slope areas and is accounted for
in Figure 5.
Exist. Drainage------- �`
f0.17ac Dev. Boundary +0.34ac Dev.
+D.71ac Exist. +0.23ac Dev. /?
// +6.150c Exist.
+0.02ac Dev. +0.21ac Exist.
TOTAL Dev. (Ultimate) drainage Area: TOTAL Ex. drainage Area:
294,76ac 293.84ac
I"
t1.38ac +0.26ac +0.97oc Dev
+0.71ac +0.28ac
f0.21ac +1.27ac I
+6.15ac +0.29ac
+5.54ac
303.21 ac +0.17ac
+0.23ac
+0.34ac Exist. Drainage
f 0.97ac Boundary
Developed Drainage Boundary +0.02ac
I
+0.26ac Dev. +1.27 303.21ac
� ac Dev. +5.54ac Dev.
I
77
\ +0.29oc Dev.
+1.38ac Exist.--, \� i
+0.28ac Dev
�J
Figure 5: Ultimate (Ult) Developed vs. Existing Drainage Area Balance
No Scale
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Spyglass Ranch Tract 35337
Hydrology Study
It may be observed that there is a slight difference between the total
developed condition drainage area and the total existing condition drainage
area (i.e. 313.91 vs. 307.65 acres). The minor difference is attributed
primarily to the proposed offsite grading slope areas and is accounted for
in Figure 4.
TOTAL Dev. (Stage 7) drainage Area: TOTAL Ex. drainage Area:
373.970c 307.65ac
+1.38aC +0.26ac
+0.28ac
315.29ac +1.27ac
+0.29ac
+5.54aC Exist. & Dev. (s9)
Drofnoge Boundary
315.29ac
I
Exist. Drainage
Developed Drainage Boundary Boundary
difference I
I
+0.26ac Dev.
� +1.27ac Dev, +5.54ac Dev.
I
+0.29oc Dev.
+1.38ac Exist. \�\ / +0.28ac Dev.
Figure 4: Stage 1 (S1) Developed vs. Existing Drainage Area Balance
No Scale
Table 3 identifies only those drainage areas that are different in the
Ultimate condition. All other drainage areas remain the same from the
Stage 1 to Ultimate condition scenarios.
Table 3: Rational Method Summary - Ultimate Condition Variable Areas
Developed Dev Ex.
Condition Area Equiv. Existing Developed Existing Total Total
(Ultimate) Condition Area Q(100yr) Q(100yr) Area Area
(Ac) (ac)
C 1 41 1 133.521 155.0 1 44.67 1 53.56
D 19 1 69.7 86.1 27.59 29.81
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Spyglass Ranch Tract 35337
Hydrology Study
Results and Summary
This study divides and models the site into sixteen existing condition
drainage areas and thirteen developed condition drainage areas. The
existing areas are designated as Areas 1 through 16, and the developed
areas are designated as Areas "A" through "M," as depicted in both the
Stage 1 and Ultimate Developed Condition Hydrology Maps. Note that for
ease of reference, the drainage area designations shown on the all the
hydrology maps and exhibits represent the same drainage areas (for
example, existing Area 9 as modeled in the rational method analysis is the
same existing Area 9 modeled in the existing unit hydrograph analysis).
As already discussed, the rational method analysis was performed on
both the Stage 1 and Ultimate condition scenarios. The node model data
flow sheets for each analysis, including the existing condition, are provided
for reference in the Exhibits section of this report. The flow rates resulting
from the rational method analysis are used in determining the volume
street flow, catch basin sizing and locations, and the storm drain pipe
necessary to achieve the design criteria. Street capacity and catch basin
design summary tables are provided in the Exhibits section of this report.
Table 2 is provided to summarize the Stage 1 condition results of the
rational method study. The table presents only the peak 100-Year flow
rate values for purposes of comparison where appropriate. Discrepancies
between Developed and Existing conditions indicated in the table, as well as
other hydrological concerns, are discussed in the sections following.
Table 2: Rational Method Summary - Stage 1 Condition
Developed Developed Existing
Condition Area
Equiv. Existing Developed Existing Total Total
(Stage 1) Condition Area Q(100yr) Q(100yr) Area (Ac) Area
(ac)
A 1 172.1 14.6 70.37 4.72
B 2 45.6 138.1 18.81 50.04
C 4 180.8 193.6 65.71 67.37
D 9 73.6 86.1 30.66 29.81
D.18 & D.19 6, 7, 8 12.2 20.9 4.68 6.60
E 12 134.0 199.4 53.18 71.12
F-G 13 55.3 64.1 27.77 21.64
H 14 32.5 39.6 10.00 12.56
I 15 11.1 7.3 2.85 2.04
J 16 34.3 29.2 10.82 9.73
K 3 5.4 36.0 2.15 11.00
L 5 28.3 31.0 12.56 W.55
M 10, 11 14.0 36.2 4.35 10.47
Totals 313.91 307.65
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Spyglass Ranch Tract 35337
Hydrology Study M
5. Main outlet Q used to confirm WSE inside baffle chamber. Q not used in
determining the route rating curve.
Tables 7 summarizes the outlet structure design for Basin #2.
Table 7: Basin #2 Outlet Structure Design Summary
Outlet Structure Openings
Number Invert
orifices Dia. or Invert elev.
or W (in) Area (sf) Elev. above Remark
H (in) (MSL) bottom
(ft)
Stage 1 4 1.5 0.049 1292.00 2.74 At baffle wall
Stage 2 5 12 3.927 1295.85 6.15 At baffle wall
Stage 3 4 8 1.396 1297.18 7.65 At baffle wall
Main Outlet 1.0 48 12.566 1291.20 0 At headwall
Baffle Wall Weir (Stage 4)
Invert Weir
elev. Crest
L (FT) Above Elev.
bottom (MSL)
(ft)
8.0 9.55 1298.75
As already discussed, there is no storm mitigation requirement at this
location since the intended outlet is the Wasson Canyon Basin, an 11MS4"
improved drainage facility owned and operated by RCFCD. However, in this
case, since the goal is to match the approved 100-Year flows in the
existing RCB culvert, the basin outlet is designed to mitigate the 100-Year
storm flows. Table 8 provides a summary of the basin detention
performance.
Table 8: Basin #2 Detention Basin Route Summary
Duration QPK3 (cfs) QPK (cfs) Max Water
QPK (cfs)
UHA into UHA out of Depth in
(hr) basin basin reduction Basin (ft)
1 168.5 72.5 96.0 7.6
Notes:
1. UHA = unit hydrograph for Area "A"
2. Q is 100-Year Strom Frequency.
3. QPK for UHA is calibrated to match the rational method Q.
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Spyglass Ranch Tract 35337
Hydrology Study M
designed to provide storm and water quality mitigation. The flow rate is
given by "Q" in cubic-feet-per-second (cfs).
Table 6: Basin #2_ - Depth vs. Outflow
WS Stage 1 Stage 2 Stage 3 Stage 4 Cumulative Main
Depth Elevation Q (cfs)' Q (cfs)2 Q (cfs)3 Q (cfs)4 Outflow Q Outlet Q
(cfs) (cfs)5
8.00 1300.00 0.74 42.37 12.42 36.61 92.13 179.49
7.50 1299.50 0.71 39.74 11.26 17.01 68.73 174.32
7.00 1299.00 0.69 36.91 9.98 3.27 50.85 168.99
6.50 1298.50 0.66 33.86 8.50 0.00 43.02 163.48
6.00 1298.00 0.64 30.50 6.70 0.00 37.83 157.78
5.50 1297.50 0.61 26.72 4.18 0.00 31.51 151.87
5.00 1297.00 0.58 22.30 0.00 0.00 22.89 145.72
4.50 1296.50 0.55 16.77 0.00 0.00 17.32 139.30
4.00 1296.00 0.52 8.06 0.00 0.00 8.58 132.56
3.50 1295.50 0.49 0.00 0.00 0.00 0.49 125.47
3.00 1295.00 0.45 0.00 0.00 0.00 0.45 117.95
2.66 1294.66 0.42 0.00 0.00 0.00 0.42 112.55
2.33 1294.33 0.40 0.00 0.00 0.00 0.40 107.05
2.00 1294.00 0.37 0.00 0.00 0.00 0.37 101.25
1.66 1293.66 0.33 0.00 0.00 0.00 0.33 94.90
1.33 1293.33 0.30 0.00 0.00 0.00 0.30 88.31
1.00 1293.00 0.26 0.00 0.00 0.00 0.26 81.18
0.66 1292.66 0.21 0.00 0.00 0.00 0.21 73.11
0.33 1292.33 0.15 0.00 0.00 0.00 0.15 64.32
Notes:
1. (4) 1.5 in. diameter orifice in exterior baffle wall, invert=1291.94.
2. (5) 12 in. diameter orifice in exterior baffle wall, invert=1295.35.
3. (4) 8 in. diameter orifice in exterior baffle wall, invert=1296.85.
4. 8 ft. wide baffle wall, TW=1298.75.
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Spyglass Ranch Tract 35337
Hydrology Study
Table A- _Basin. ##2 - Vo-lume V-s Depth
1296.50 41400 20200 117678 2.7015 4.50
1296.00 39400 19250 97478 2.2378 4.00
1295.50 37600 17475 78228 1.7959 3.50
1295.00 32300 10478 60753 1.3947 3.00
1294.66 31200 9983 50276 1.1542 2.66
1294.33 29300 9207 40293 0.9250 2.33
1294.00 26500 8168 31086 0.7136 2.00
1293.66 23000 6947 22919 0.5261 1.66
1293.33 19100 5693 15972 0.3667 1.33
1293.00 15400 4439 10280 0.2360 1.00
1292.66 11500 3284 5841 0.1341 0.66
1292.33 8400 2558 2558 0.0587 0.33
1292.00 7100 0 0 0.0000 0.00
Table 5: Basin #2 - Volume Vs. Depth for Water Quality'
Contour Contour Volume Total Total Volume Basin
Elevation Area (CF) Volume (Acre-FT) Depth
(SF) (C F) (FT)
1296.00 39400 19250 97478 2.2378 4.00
1295.50 37600 17475 78228 1.7959 3.50
1295.00 32300 10478 60753 1.3947 3.00
1294.66 31200 9983 50276 1.1542 2.66
1294.33 29300 9207 40293 0.9250 2.33
1294.00 26500 8168 31086 0.7136 2.00
1293.66 23000 6947 22919 0.5261 1.66
1293.33 19100 5693 15972 0.3667 1.33
1293.00 15400 4439 10280 0.2360 1.00
1292.66 11500 3284 5841 0.1341 0.66
1292.33 8400 2558 2558 0.0587 0.33
1292.00 7100 0 0 0.0000 0.00
VBMP = 72890 1.6733
VBMP Water Depth = 3.4
Notes:
1. Volumes shown use the upper and bottom stages of basin. Forebay
volume is not included in the computations.
Table 6 provides a summary of Basin ##2 Depth vs. Outflow, as utilized in
the routing analysis. Note that the basin has an outlet structure that is
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Spyglass Ranch Tract 35337
Hydrology Study
The following sections provide a brief description of each drainage area
and the drainage basins along with the general results and computation
summaries. The hydrology computations and output files are provided in
the Appendix of this report.
Area "A" and Basin #2
Area "A" is a major drainage area in the post-developed condition that
is comprised of about half of the west side of the site. The closest
comparable drainage area in the pre-developed, or existing condition based
upon the drainage outlet is Area 1. One may observe that Area 1 is much
smaller than Area "A". This is due to the proposed onsite grading that
causes a large portion of the existing drainage area that is tributary to
the adjacent downstream property to the west, PM 30985, to be redirected
to the Spyglass Ranch drainage basin, which is near the existing Area 1
outlet point. This localized diversion is not an issue for three reasons: (1)
the onsite basin is designed to detain the increased runoff from the
drainage area, (2) the reduced runoff received to PM 30985 does not create
a potential adverse condition, and (3) the runoff from this area is
discharged to the Wasson Canyon Basin, a publically owned drainage facility.
Area "A" is completely tributary to Basin #2. The higher storm runoff
that enters the basin from this drainage area is mitigated at a ratio of
about 0.6 to 1 - in other words the basin can detain about 60% of the
volumetric flow rate delivered to it. The runoff from this area will drain
through the detention basin and into the existing 61x5' RCB culvert through
the basin's outlet pipe located in Camino Del Norte. The basin is sized to
retard the necessary flow such that the approved overall total flow rate of
the existing RCB culvert is not exceeded. Basin #2 is also designed as a
water quality facility that will treat the first flush flows from the entire
tributary area as required by NPDES guidelines.
Table 4 provides a summary of Basin #2 Volume vs. Depth relationship,
as utilized in the routing analysis. Table 5 provides a similar summary of
Basin #2 Volume vs. Depth relationship, except as related to the required
water quality treatment.
Table 4: Basin #2 - Volume Vs. Depth
Contour Contour Volume Total Total Basin
Elevation Area (CF) Volume Volume Depth
(SF) (CF) (Acre-FT) (FT)
1300.00 55600 27275 287028 6.5893 8.00
1299.50 53500 26225 259753 5.9631 7.50
1299.00 51400 25200 233528 5.3611 7.00
1298.50 49400 24175 208328 4.7826 6.50
1298.00 47300 23150 184153 4.2276 6.00
1297.50 45300 22150 161003 3.6961 E5.50
1297.00 43300 21175 138853 3.1876 5.00
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Spyglass Ranch Tract 35337
Hydrology Study \`y
required for this sub—area. Tables 2 and 3 provide a complete summary of
the rational method analysis for each drainage area.
Basin Spillways and Auxiliary Outlets
In the event that any of the basins do not drain properly, each
basin is equipped with an emergency spillway. The concrete lined spillway
for Basin #1, an infiltration basin, is located on the easterly side of the
basin adjacent to Elsinore Hills Road. The spillway is set just above the
design water surface elevation and is sized to manage the maximum
flowrate that is designed to bifurcate into the basin plus any additional
runoff that is directly tributary to the basin. In addition to the spillway,
an emergency outlet pipe with a shear gate is provided near the basin
bottom in the event that standing water would need to be drained for any
reason.
The concrete lined spillway for Basin #2, a dual purpose extended
detention basin, is located on the westerly side of the basin adjacent to
Camino Del Norte. The spillway is set above the outlet structure baffle
wall weir and is sized to manage the maximum design flowrate tributary to
the basin. The outlet structure provides a shear gate clean out in the
event that standing water would need to be drained for any reason.
The concrete lined spillway for Basin #3, a dual purpose extended
detention basin, is located on the southerly side of the basin adjacent to
the south tract boundary. The spillway is set above the outlet structure
baffle wall weir and is sized to manage the maximum design flowrate
tributary to the basin. The outlet structure provides a shear gate clean out
in the event that standing water would need to be drained for any reason.
The critical hydraulic routing calculations for the spillways are
provided in the Appendix of this report.
— Conclusion —
The projected flows that will be discharged to the existing properties
and facilities downstream of the proposed development are permissible
within the criteria and specifications indicated in this study and satisfy the
City conditions of approval for increased runoff criteria. All tributary
offsite flows are either mitigated to match the historic flows, or conveyed
to a public drainage facility, or accepted by the receiving property via a
joint development agreement (drainage acceptance agreement).
The three onsite basins are designed to provide the necessary water
quality treatment to be in compliance with NPDES guidelines and
regulations. Two of the three onsite basins are also designed for storm
mitigation based upon the increased runoff criteria for the 10—Year storm
frequency at the 6 hour and 24 hour storm durations. The proposed
streets and storm drain system provide sufficient capacity to manage all
10—year and 100—year flows at their required limits per the Conditions of
Approval. Overall, the entire site is designed to safely convey and manage
the runoff from the 100—year storm frequency.
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Spyglass Ranch Tract 35337
Hydrology Study
developed condition peak flow rate of Area 3. It follows, consequently, that
no storm mitigation is required for this drainage area. Tables 2 and 3
provide a complete summary of the rational method analysis for each
drainage area.
Area "L" (JDA Area
Area "L" is a drainage area in the post—developed condition that is
tributary to the adjacent downstream property to the north, namely South
Shore (see Figure 6). Under the Stage 1 condition, the area is comprised
largely of natural area with manufactured slope area. Under the Ultimate
condition, the area is comprised of one—quarter acre residential and estate
lot residential developments. The comparable drainage area in the pre—
developed, or existing condition is Area 5.
Since, Area "L" is impacted differently under each of the Stage 1 and
Ultimate scenarios, this study evaluates the drainage area under both
scenarios in order to determine the more critical condition. In short, the
Stage 1 developed condition will generate a lower tributary area than the
Ultimate developed condition will generate at the drainage area's outlet
point. Both of these conditions exceed the tributary area in the existing
condition. Under the Stage 1 scenario, the drainage course of Area "L" is
released at the north Spyglass Ranch boundary at the existing drainage
course that continues northerly onto the South Shore property. Under the
Ultimate condition, the developed condition storm flows from this drainage
area will connect to the South Shore storm drain system to be conveyed to
the South Shore drainage basin.
Due to topographical and other constraints, Area "L" is resolved in
the JDA by a drainage acceptance agreement on the part of South Shore
and to the benefit of Spyglass Ranch. In other words, it is mutually
agreed upon that there is no requirement for Spyglass Ranch to mitigate
for any incremental increase in runoff due to development that may enter
the South Shore property as a result of Spyglass Ranch developing its
property. The JDA stipulates that South Shore will accept all of the
tributary developed area from Spyglass Ranch. South Shore will convey and
provide the necessary water quality treatment to these storm flows prior to
the waters being discharged to Wasson Canyon Creek.
Area "M"
Area ''M" is a drainage area located along a portion of the Spyglass
Ranch south property line in the post—developed condition that is tributary
to the adjacent downstream properties to the south. For the most part,
this drainage area is comprised of manufactured slope area. The
comparable drainage areas in the pre—developed, or existing condition are
Areas 10 and 11. Area "M" developed condition drainage area produces a
lower tributary drainage area when combined and compared to the
correlating existing condition drainage areas. The rational analysis
indicates that the total developed condition peak flow rate of Sub—Area "M"
is less than half that of the total pre—developed condition peak flow rate
of Areas 10 and 11. It follows, consequently, that no storm mitigation is
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Spyglass Ranch Tract 35337
Hydrology Study
the low flows originate on natural ground, water quality treatment is not
necessary for this area. The higher storm flows are designed to discharge
into the existing 30" culvert located in Camino Del Norte. The rational
analysis indicates that the developed condition peak flow rate of Areas "H"
is less than the total pre—developed condition peak flow rate of Area 14.
It follows, consequently, that the capacity of the existing culvert will not be
exceeded and therefore no storm mitigation is required for this area.
Tables 2 and 3 provide a complete summary of the rational method
analysis for each drainage area.
Area "I"
Area "I" is a minor drainage area in the post—developed condition that
is comprised of less than three acres of roadway and manufactured slope
area. The comparable drainage area in the pre—developed, or existing
condition is Area 15, which similarly is roadway and manufactured slope
area. The low flows from this area are designed to be treated within the
catch basin via a catch basin filter or other similar water quality
treatment device. The higher storm flows are designed to discharge into
the existing 18" culvert located in Camino Del Norte. The rational analysis
indicates that the developed condition peak flow rate of Area "I" is well
within the capacity of the existing culvert and therefore no storm
mitigation is required for this area. Tables 2 and 3 provide a complete
summary of the rational method analysis for each drainage area.
Area '°J"
Area "J" is a drainage area in the post—developed condition that is
primarily comprised of natural area. The comparable drainage area in the
pre—developed, or existing condition is Area 16. Since the vast majority of
the low flows originate on natural ground, water quality treatment is not
necessary for this area. The higher storm flows are designed to discharge
into the existing 30" culvert located in Camino Del Norte. The rational
analysis indicates that the developed condition peak flow rate of Area "J" is
well within the capacity of the existing culvert and therefore no storm
mitigation is required for this area. Tables 2 and 3 provide a complete
summary of the rational method analysis for each drainage area.
Area "K"
Area "K" is a minor drainage area in the post—developed condition that
is primarily comprised of manufactured slope area near the north property
line of Spyglass Ranch. The comparable drainage area in the pre—
developed, or existing condition is Area 3. Since the developed area is less
than one acre, water quality treatment is not necessary for this area.
Storm runoff from Area "K' will drain onto the adjacent downstream
property to the north, referred to as the Eichorn Property for purposes of
this report. In the developed condition, the area tributary to the Eichorn
Property is much smaller when compared to the correlating existing
condition drainage area. The rational analysis indicates that the total
developed condition peak flow rate of Area °°K" is less than the total pre—
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Spyglass Ranch Tract 35337
Hydrology Study
area. Tables 2 and 3 provide a complete summary of the rational method
analysis for each drainage area.
Table 16 provides a summary of Basin #1 Volume vs. Depth relationship,
as related to the required water quality treatment.
Table 16: Basin #1 — Volume Vs. Depth for Water Quality
Contour Contour Volume Total Total Volume Basin
Elevation Area (CF) Volume (Acre—FT) Depth
(SF) (CF) (FT)
1400.00 36800 36200 176600 4.0542 4.50
1399.50 35600 34950 140400 3.2231 4.00
1399.00 34300 33100 105450 2.4208 3.50
1398.00 31900 30700 72350 1.6609 2.50
1397.00 29500 28350 41650 0.9562 1.50
1396.00 27200 13300 13300 0.3053 0.50
1395.50 26000 0 0 0.0000 0.00
Vbmp = 71400 1.6391
Vbmp Water Depth = 2.5
Areas ,F,, and "G"
Areas 'IF" and "G" are drainage areas in the post—developed condition
that are primarily comprised of park site and commercial land use. The
comparable drainage area in the pre—developed, or existing condition is
Area 13. The low flows that require water quality treatment for this area
originate from the park site and commercial site building pad. Since the
site plans for these parcels are not available at this time, the impervious
fraction cannot be calculated accurately. Accordingly, the applicable BMP
devices will be designed and installed in accordance with NPDES guidelines
at the time the site plans are proposed for these developments. These
water quality treatment facilities are anticipated to be located within the
park site and within the commercial development.
The higher storm flows are designed to discharge into the existing 36"
and 18" culverts located in Camino Del Norte. The rational analysis
indicates that the combined developed condition peak flow rates of Areas
'IF" and "G" are less than the total pre—developed condition peak flow rate
of Area 13. It follows, consequently, that the capacity of the existing
culvert will not be exceeded and therefore no storm mitigation is required
for this area. Tables 2 and 3 provide a complete summary of the rational
method analysis for each drainage area.
Area "H"
Area "H" is a drainage area in the post—developed condition that is
primarily comprised of natural area. The comparable drainage area in the
pre—developed, or existing condition is Area 14. Since the vast majority of
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Spyglass Ranch Tract 35337
Hydrology Study
Table 15: Basin #3 Detention Basin Route Summary
Duration QPK (cfs) UHD QPK (cfs) QPK (cfs) Max Water
(hr) into basin UHD out of reduction Depth in
basin Basin (ft)
6 31.0 16.3 14.7 4.6
24 9.5 8.4 1.1 1 3.4
Notes:
1. UHD = unit hydrograph for Area "D"
2. Q is 10—Year Strom Frequency.
Area "D" contains minor sub—areas 11D.18" and "D.19," which are located
along the east Spyglass Ranch boundary, that are comprised of natural
area and manufactured slope area. These minor sub—areas are correlated
to existing Areas 6, 7, and 8 for purposes of comparison. These areas are
not tributary to Basin #3, as is the main portion of Area "D." These areas
will drain to the east onto the adjacent downstream property, Tract 32013.
The minor developed condition sub—areas produce a lower tributary
drainage area when combined and compared to the correlating existing
condition drainage areas under both the Stage 1 and Ultimate scenarios.
The rational analysis indicates that the total developed condition peak flow
rate of Sub—Areas "D.18" and ,D.19" is less than the total pre—developed
condition peak flow rate of Areas 6, 7, and 8. It follows, consequently,
that no storm mitigation is required for these sub—areas.
Area "E"and Basin-4
Area "E" is a major drainage area in the post—developed condition that
is comprised of one—quarter acre residential development, multi—family
development, and commercial land use. The comparable drainage area in
the pre—developed, or existing condition is Area 12. The first flush, or low
storm flows for Area "E" will be designed to bifurcate into Basin #1 for
water quality treatment. Because there is a favorable percolation rate at
this site, Basin #1 is designed as an infiltration basin. The percolation
rate based upon the percolation evaluation that was performed at the basin
site is 5 minutes—per—inch.' The corresponding design infiltration rate
based upon RCFCD guidelines is 2.37 inches—per—hour. The complete basin
design worksheets are provided in the WQMP.
The high storm flows are designed to discharge into the existing 54"
culvert located in Camino Del Norte. The post—developed tributary area is
significantly less than the pre—developed area to the same outlet point.
The rational analysis indicates that the total developed condition peak flow
rate of Area "E" is less than the total pre—developed condition peak flow
rate of Area 12. By in large, this is due to the reduced drainage area in
the post—developed condition that is being conveyed to the existing 54"
culvert. It follows, consequently, that the capacity of the existing culvert
will not be exceeded and therefore no storm mitigation is required for this
t Ref: "Limited Percolation Evaluation," by GeoTek, Inc. prepared July 22, 2009.
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Spyglass Ranch Tract 35337
Hydrology Study
Table 13: Basin #3 - Depth vs. Outflow
1.96 1586.66 0.121 0.00 0.00 0.12 61.45
1.63 1586.33 0.111 0.00 0.00 0.11 58.26
1.30 1586.00 0.099 0.00 0.00 0.10 54.88
0.96 1585.66 0.085 0.00 0.00 0.08 51.17
0.63 1585.33 0.069 0.00 0.00 0.07 47.28
0.30 1585.00 0.047 0.00 0.00 0.05 43.05
Notes:
1. (3) 1 in. dia. orifices in exterior baffle wall, invert elev=1584.66.
2. (3) 12 in. dia. orifices in exterior baffle wall, invert elev=1587.15.
3. 6 ft. wide baffle wall structure, top wall elev=1590.00.
4. Main outlet Q used to confirm WSE inside baffle chamber. Q not used in
determining the route rating curve.
Tables 14 summarizes the outlet structure design for Basin #3.
Table 14: Basin #3 Outlet Structure Design Summary
Outlet Structure Orifices (Stages 1 and 2)
Invert
Number Invert elev.
of Dia. (in) Area Elev. above Remark
orifices (sf) (MSL) bottom
(ft)
Stage 1 3 1.0 0.016 1584.70 2.76 At baffle wall
Stage 2 3 12.0 2.356 1587.65 5.25 At baffle wall
Main 1 36 7.069 1583.40 0 At headwall
Outlet
Baffle Wall Weir (Stage 3)
Invert Weir
elev. Crest
L (FT) above Elev.
bottom (MSL)
(ft)
6.0 8.10 1590.00
Basin #3 is designed to maintain a minimum freeboard of 1.0' and
maximum freeboard of 2.0' from the spillway crest elevation. Table 15
provides a summary of the basin detention performance.
K: \265324\Final\llydro1ogy\12cport\324 Report 13ody.doex - 22 -
Spyglass Ranch Tract 35337
Hydrology Study
Table 12: Basin #3 - Volume Vs. Depth for Water Qualityl
Contour Contour Volume Total Total Volume Basin
Elevation Area (CF) Volume (Acre-FT) Depth
(SF) (CF) (FT)
1587.33 15700 4670 24456 0.5614 2.63
1587.00 12600 4043 19787 0.4542 2.30
1586.66 11900 3828 15744 0.3614 1.96
1586.33 11300 3581 11916 0.2736 1.63
1586.00 10400 3102 8336 0.1914 1.30
1585.66 8400 2393 5234 0.1201 0.96
1585.33 6100 1716 2841 0.0652 0.63
1585.00 4300 1125 1125 0.0258 0.30
1584.70 3200 0 0 0.0000 0.00
Vbmp = 21600 0.4959
Vbmp Water Depth = 2.4
Notes:
1. Volumes shown use the upper and bottom stages of basin. Forebay
volume is not included in the computations.
Table 13 provides a summary of Basin #3 Depth vs. Outflow, as utilized in
the routing analysis. Note that the basin has an outlet structure that is
designed to provide storm and water quality mitigation.
Table 13: Basin #3 - Depth vs. Outflow
WS Stage 1 Stage 2 Stage 3 Cumulative Main
Depth Elevation Q (cfs)l Q (cfs)2 Q (cfs)3 Outflow Q Outlet Q
(cfs) (cfs)4
6.80 1591.50 0.226 24.49 37.15 61.86 96.87
6.30 1591.00 0.218 22.84 20.22 43.28 93.83
5.80 1590.50 0.209 21.07 7.15 28.43 90.69
5.30 1590.00 0.200 19.13 0.00 19.33 87.44
4.96 1589.66 0.193 17.69 0.00 17.89 85.16
4.63 1589.33 0.186 16.18 0.00 16.36 82.88
4.30 1589.00 0.180 14.50 0.00 14.68 80.54
3.96 1588.66 0.172 12.54 0.00 12.71 78.06
3.63 1588.33 0.165 10.29 0.00 10.46 75.57
3.30 1588.00 0.157 7.38 0.00 7.54 73.00
2.96 1587.66 0.149 1.25 0.00 1.40 70.25
2.63 1587.33 0.141 0.00 0.00 0.14 67.47
2.30 1587.00 0.131 0.00 0.00 0.13 64.58
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Spyglass Ranch Tract 35337
Hydrology Study hI ^
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The higher storm runoff that enters the basin from this area is
mitigated for the 10-Year storm in accordance with the Conditions of
Approval. The entire runoff from this sub-area is designed to drain into
the detention basin and onto to the adjacent downstream property to the
south through the basin's outlet pipe. The basin is sized to retard the
necessary flow such that the overall required historic flow rates tributary
to that property are not exceeded (i.e. 6 and 24 hour storm durations for
the 10-Year storm frequency). Basin #3 is also designed as a water
quality facility that will treat the first flush flows from the entire tributary
area as required by NPDES guidelines.
Table 11 provides a summary of Basin #3 Volume vs. Depth relationship,
as utilized in the basin routing analysis. Table 12 provides a similar
summary of Basin #3 Volume vs. Depth relationship, except as related to
the required water quality treatment.
Table 11: Basin #3 Volume Vs. I?cth
Contour Contour Volume Total Total Basin
Elevation Area (SF) (CF) Volume Volume Depth
(CF) (Acre-FT) (FT)
1591.50 28000 13600 114130 2.6201 6.80
1591.00 26400 12800 100530 2.3079 6.30
1590.50 24800 12025 87730 2.0140 5.80
1590.00 23300 7524 75705 1.7379 5.30
1589.66 22300 7194 68181 1.5652 4.96
1589.33 21300 6864 60987 1.4001 4.63
1589.00 20300 6551 54123 1.2425 4.30
1588.66 19400 6237 47573 1.0921 3.96
1588.33 18400 5924 41336 0.9489 3.63
1588.00 17500 5627 35412 0.8129 3.30
1587.66 16600 5330 29786 0.6838 2.96
1587.33 15700 4670 24456 0.5614 2.63
1587.00 12600 4043 19787 0.4542 2.30
1586.66 11900 3828 15744 0.3614 1.96
1586.33 11300 3581 11916 0.2736 1.63
1586.00 10400 3102 8336 0.1914 1.30
1585.66 8400 2393 5234 0.1201 0.96
1585.33 6100 1716 2841 0.0652 0.63
1585.00 4300 1125 1125 0.0258 0.30
1584.70 3200 0 0 0.0000 0.00
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Spyglass Ranch Tract 35337
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scenarios in order to determine the required interim and ultimate
condition facilities. In short, the developed condition storm flows will be
discharged to the matching existing drainage course under the Stage 1
condition and conveyed to the west to join the Wasson Canyon Creek.
Under the Ultimate condition, the developed condition storm flows from this
drainage area will connect to the South Shore storm drain system to be
conveyed to the South Shore drainage basin.
Area "D" and Basin #3
Area "D" is a significant drainage area in the post-developed condition
that is comprised of one-quarter acre residential development in the
south-easterly vicinity of the site. The primary comparable drainage area
in the pre-developed, or existing condition is Area 9. This area is entirely
tributary to Basin #3.
Since, Area "D" is impacted differently under each of the Stage 1 and
Ultimate scenarios, this study evaluates the drainage area under both
scenarios in order to determine the more critical condition. In short, the
Stage 1 developed condition will generate a higher tributary area than the
Ultimate developed condition will generate at the drainage area's outlet
point. Therefore, the Stage 1 scenario drainage area is used in modeling
the unit hydrograph for Area D (UHD) that is used in the basin routing
analysis.
The unit hydrograph analysis for this sub-area is evaluated for two
areas: (1) Unit Hydrograph "D" (UHD) for the Stage 1 Grading Design, and
(2) UHD for the Stage 1 Grading Design Tributary to Basin #3. UHD under
the first condition generates a higher tributary area to the adjacent
downstream development primarily due to the offsite grading in that
vicinity. Accordingly, the first hydrograph is used in comparison with the
Existing Condition Unit Hydrograph 9 (UH9) in order to determine the total
required mitigation. The second hydrograph is used in the basin routing
analysis to determine the detention basin performance. Exhibits for each
of the hydrographs are provided in the Exhibits section of this report.
Table 10 provides a summary of the existing vs. proposed hydrograph
results and the corresponding Q reduction required in order to match the
historic flows.
Table 10: Unit Hydrograph Summary - 10-Year Storm Frequency
Duration QPK (cfs) UH9' QPK (cfs) UHD2 Required QPK (cfs)
(hr) (Existing) (Proposed) reduction
6 32.8 35.0 2.2
24 10.7 10.7 NIL
Notes:
1. UH9 = Unit hydrograph for Area 9.
2. UHD = Unit hydrograph for Area I'D" under Stage 1 Grading Design.
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Spyglass Ranch Tract 35337
Hydrology Study
prepared for the multi—family development. These water quality treatment
devices are anticipated to be located within the multi—family development.
Area "C" (JDA Area)
Area "C" is a major drainage area in the post—developed condition that
is comprised of about half of the east side of the site. The comparable
drainage area in the pre—developed, or existing condition is Area 4. This
area is tributary to the adjacent downstream property to the north, namely
Tract 31593, South Shore (see Figure 6).
TRACT 31593
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TRACT 35337
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Figure 6: Developed Areas Tributary to Tract 31593
No Scale
The drainage course of Area 4 exits and enters the Spyglass Ranch
north property line at multiple locations, making it difficult to meaningfully
compare pre—developed and post—developed flow rates. Largely due to the
convoluted nature of Area 4, this drainage area presents a special condition
that is resolved by a drainage acceptance agreement on the part of South
Shore and to the benefit of Spyglass Ranch as part of the overall joint
development agreement (JDA) between the two projects. In other words, it
is mutually agreed upon that there is no requirement for Spyglass Ranch
to mitigate for any incremental increase in runoff due to development that
may enter the South Shore property as a result of Spyglass Ranch
developing its property. The JDA stipulates that South Shore will accept all
of the tributary developed area from Spyglass Ranch. South Shore will
convey and provide the necessary water quality treatment for these storm
flows prior to the waters being discharged to Wasson Canyon Creek.
Since, Area "C" is impacted differently under each of the Stage 1 and
Ultimate scenarios, this study evaluates the drainage area under both
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Spyglass Ranch Tract 35337
Hydrology Study
Per the PM 30985 grading and improvement plans, the approved design Q
for the existing RCB culvert is 185 cfs in the Spyglass Ranch pre—developed
condition. In the Spyglass Ranch post—developed condition, the total Q
delivered to the existing RCB culvert is 181 cfs, which is within the
approved design Q of 185 cfs. Table 9 summarizes the total resulting flows
entering the existing RCB culvert in the proposed condition.
Table 9: Post—developed Q Summary to Existing RCB Culvert
Hydrology Q
Runoff Source Description Map Node (cfs)
Number
PM 30985 Onsite Runoff n/a 40
Spyglass Area "A" (Basin #2 outlet)' 0.120 73
Spyglass Area KB" via PM 30985 0.202 43
Spyglass Minor Runoff 207;209 3
Street runoff (catch basins at PM 30985) n/a 18
Street runoff 144 4
Total Q to RCB Culvert: 181
Notes:
1. Q shown from Basin #2 outlet is post mitigation.
Area KB"
Area "B" is a significant drainage area in the post—developed condition
that is comprised of a multi—family parcel and an offsite tributary area.
The closest comparable drainage area in the pre—developed, or existing
condition based upon the drainage outlet is Area 2. One may observe that
Area 2 is much larger than Area "B". This is due to the proposed onsite
grading that causes a large portion of the existing drainage area that is
tributary to PM 30985 to be redirected to the Spyglass Ranch drainage
basin and away from the existing Area 2 outlet point at the common
boundary.
The post—developed runoff from this area will drain onto PM 30985, as it
does in the existing condition. PM 30985 is to provide a storm drain inlet
structure to intercept this runoff. The peak flow rate in the developed
condition that will discharge to PM 30985 at the common boundary is 43
cfs, which is significantly less than both the historic flow rate at that
location, and the approved flow rate anticipated by PM 30985 of 128 cfs.
Therefore, no mitigation is required at this location. Tables 2 and 3 provide
a complete summary of the rational method analysis for each drainage
area.
The low flows that require water quality treatment for this area
originate primarily from the multi—family building pad. Since the site plan
is not available at this time, the impervious fraction cannot be calculated
accurately. Accordingly, the applicable BMP devices will be designed and
installed in accordance with NPDES guidelines at the time the site plan is
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