HomeMy WebLinkAboutCT 2018-0005; VILLAGE WALK; DRAINAGE STUDY; 2018-05-23--... .... -..
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DRAINAGE STUDY
For
VILLAGE WALK
CT2018-0005
Prepared for:
OMS Consultants, Inc .
123 71 S Lewis St #203
Garden Grove, CA 92840
(714) 740-8840
Prepared by:
R·E·C
Consultants, Inc .
Dr. Luis Parra
REC Consultants, Inc
27349 Jefferson Ave, Suite 112
Temecula, CA 92590
Telephone: 951-693-2400
Report Prepared:
May 23, 2018
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MAY 3 0 2018
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Village Walk
Drainage Study
TABLE OF CONTENTS
Chapter 1 -Executive Summary
1.1 Introduction
1.2 Summary of Existing Conditions
1.3 Summary of Proposed Condition
1.4 Summary of Results
1.5 Hydraulic Analysis
1.6 Conclusions
Chapter 2 -Methodology
2.1 County of San Diego Drainage Design Criteria
2.2 Hydrograph Development Summary
(from San Diego County Hydrology Manual)
Chapter 3 -Existing Condition 100-Year Hydrologic Analysis
Chapter 4-Developed Condition 100-Year Hydrologic Analysis
Chapter 5 -Modified-Puls Detention Routing (HEC-HMS)
5.1 Rational Method Hydrographs
5.2 Stage-Storage & Stage-Discharge Relationships
5.3 HEC-HMS Modified-Puls Routing Results
Chapter 6 -WSPG Hydraulic Analysis
Chapter 7 -Hydrology Exhibits
SECTION
II
Ill
IV
V
VI
VII
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Village Walk
Drainage Study
CHAPTER 1 -EXECUTIVE SUMMARY
1.1 -Introduction
111 The Village Walk project site is located to the south of Oak Avenue in the City of
Carlsbad, California .
.,. Runoff from the site drains to a single point of discharge from the project site, the
existing storm drain located within the adjacent Oak Avenue to the north of the existing
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This study analyzes existing and developed condition 100-year peak flowrates from the
development to the existing point of discharge .
The project site lies outside any FEMA 100-year floodplain zones. Therefore, no Letters
of Map Revision will be required.
Treatment of storm water runoff from the site has been addressed in a separate report -
the "Storm Water Quality Management Plan for Village Walk", dated February 2018 by
REC.
Per County of San Diego drainage criteria, the Modified Rational Method should be
used to determine peak design flowrates when the contributing drainage area is less
than 1.0 square mile. Since the total watershed area discharging from the site is less
than 1.0 square mile, AES computer software was used to model the pre & post
developed condition runoff response per the Modified Rational Method.
Methodology used for the computation of design rainfall events, runoff coefficients, and
rainfall intensity values are consistent with criteria set forth in the "County of San Diego
Drainage Design Manual". A more detailed explanation of methodology used for this
analysis is listed in Chapter 2 of this report .
Developed condition peak flows were calculated using AES. The corresponding
hydrographs were generated using the RickRat Hydro program by Rick Engineering.
Hydraulic Modified-Puls detention basin routing of the AES rational method hydrology
was performed using the Army Corps of Engineers HEC-HMS 4.1 software.
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Drainage Study
1.2 -Summary of Existing Conditions
In existing conditions, the Village Walk project site is an existing residential lot with
associated structures and pavement.
Runoff from the existing site drains via overland flow to the existing storm drain system
located to the north of the project site within the adjacent Oak Avenue .
Per County of San Diego rainfall isopluvial maps, the design 100-year rainfall depth for
,,,. the project site is 2.6 inches. The project site comprises of hydrologic soil class B soils
1111 such that a runoff coefficient of 0.25 was used for the vegetated areas. The existing site
has an approximate impervious footprint of 8,574 square feet. Per the equation
,,_ identified in Section 3.1.2 of the San Diego County Hydrology Manual: ..
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C = 0.9 X (%Impervious)+ Cp X (1 -% Impervious)
where Cp is the pervious runoff value (in this case, 0.25), the existing condition runoff
coefficient is 0.58. Table 1 below summarizes the existing condition design 100-year
peak flow from the project site .
Table 1 -SUMMARY OF EXISTING CONDITIONS FLOWS
Drainage Runoff 100-Year
Discharge Location Area Coefficient Peak Flow
IAcl (C) (cfs)
Oak Avenue 0.4 0.58 1.18
1.3 -Summary of Developed Conditions
The Village Walk project proposes the construction of 8 multi-family homes, inclusive of
an underground parking lot and associated landscaping. Runoff from the project is
drained to a receiving dual purpose detention basin to the southeast corner of the
project site. Mitigated peak flows are then drained from the detention facility by an 8-
inch PVC storm drain to connect to the existing storm drain located within the adjacent
Oak Avenue to the north of the project site. Runoff draining towards the underground
parking lot is intercepted by a trench drain and then pumped to the aforementioned
detention basin.
Per County of San Diego rainfall isopluvial maps, the design 100-year rainfall depth for
the project site is 2.6 inches. The project site comprises of hydrologic soil class B soils
such that a runoff coefficient of 0.25 was used for the vegetated areas. The developed
site has an approximate impervious footprint of 11,701 square feet. Per the equation
identified in Section 3.1.2 of the San Diego County Hydrology Manual the developed
condition runoff coefficient is 0.72. Table 2 summarizes the unmitigated developed
condition design 100-year peak flow from the project site.
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Table 2 -SUMMARY OF UNMITIGATED -DEVELOPED CONDITIONS FLOWS
Drainage Runoff 100-Year
Discharge Location Area Coefficient Peak Flow
IAcl (Cl (cfs)
Oak Avenue 0.4 0.72 1.41
*=Weighted C coefficient used, see AES output for calculat1ons.
Prior to discharging from the project site, first flush runoff will be treated via an onsite
infiltration BMP in accordance with standards set forth by the Regional Water Quality
Control Board and the County of San Diego's BMP Design Manual (see "Storm Water
Quality Management Plan for Village Walk").
Runoff from the developed site drains to a single onsite multiple purpose detention
basin. Peak flows are mitigated via this facility prior to discharging to the existing point
of discharge from the project site. A summary of the detention basin is provided in
Table 3.
Notes:
Table 3 -SUMMARY OF BMP BASIN DIMENSIONS
DIMENSIONS
Basin Depth to First Depth to Riser Weir Total Surface
Surface Outlet (ft)(1l Invert (ftfl Perimeter Depth(4l (ft) Lenath(3l lftl
Basin 1 0.5 1.5 8 2.0
(1): It is assumed WQ volume to be stored below this elevation, only volume above this invert is available for QlOO routing.
(2): Depth of ponding beneath riser structure's surface spillway.
(3): Overflow length, the internal perimeter of the riser.
(4): Total surface depth of BMP from top crest elevation to surface invert.
The developed condition peak flows were calculated using the modified rational. The
corresponding hydrographs were generated using the RickRat Hydro program by Rick
Engineering (a 10 minute time step was used to generate the hydrograph as HMS only
has time step allowances for 1,2,3,4,5,6 and 10 minute increments). This hydrograph
was then routed through the proposed on-site detention facility in HEC-HMS. The HMS
Modified-Puls results are summarized in Table 4.
It should be noted that as a conservative design approach, it has been assumed that
the design capture volume was stored in the detention basin prior to the routing of the
100-year event storm, as such, all volume provided beneath the first surface outlet is
not accounted for in the routing calculation .
Rational method hydrographs, stage-storage, stage-discharge relationships, outlet
structure configurations and HEC-HMS model output is provided in Chapter 5 of this
report. Table 4 summarizes the peak inflow and discharge from the detention facility.
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Table 4 -SUMMARY OF DETENTION BASIN ROUTING
Detention Basin 100-Year Peak 100-Year Peak Peak Water Surface
Inflow (cfs\ Outflow (cfs) Elevation<1> (ft\
Basin 1 1.41 0.86 1.0
Notes: (1) Elevation above the first surface inlet invert .
1.4 -Summary of Results
Table 5 summarizes developed and existing condition drainage areas and resultant
100-year peak flow rates at the receiving discharge location from the Village Walk site .
Per County of San Diego rainfall isopluvial maps, the design 100-year rainfall depth for
the site area is 2.6 inches .
Table 5 -SUMMARY OF PEAK FLOWS
Discharge Area (ac) 100 Year Peak Flow (cfs)
Location Existina Developed Difference Existina Developed Difference
Oak Avenue 0.4 0.4 0.00 1.18 0.87 -0.31
As illustrated in Table 5, the proposed Village Walk project site will reduce peak flows at
all point of discharge from the project site when compared to the existing condition. The
total net reduction in flow from the pre-developed condition is approximately 0.31 cfs .
All developed runoff will receive water quality treatment in accordance with the site
specific SWQMP.
Final design details will be provided at the final engineering phase of the development.
1.5 -Hydraulic Analysis
Runoff from the project site is to be drained to the existing storm drain located within the
adjacent Oak Avenue by a proposed 8-inch PVC storm drain .
Public Works Department of City of Carlsbad has indicated that they have been unable
to locate the improvement plans for existing 18-inch storm drain located in Oak
Avenue. This storm drain originates at Lincoln Avenue, approximately 270 feet west of
project site and drains easterly. In the absence of any record information and
considering the project site is only 270 feet from beginning of storm drain system a HGL
of 43.05 feet being the top of existing 18-inch pipe has been used as control.
In order to assess the proposed 8-inch storm drain design capacity, hydraulic analysis
was undertaken using the WSPG computer program. The computed HGL is provided in
Chapter 6 of this report.
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1.6 -Conclusions
This report has been prepared in accordance with the County of San Diego Hydrology
Manual. This report has evaluated and addressed the potential impacts and proposed
mitigation measures. A summary of the facts and findings associated with this project
and the measures addressed by this report is as follows:
• The project will not alter drainage patterns on the site or increase runoff after
development.
• The ultimate discharge points will not be changed.
• Graded areas and slopes will be hydroseeded to reduce or eliminate
sediment discharge .
• Identify and discuss, with appropriate backup/research information, the
following question item by item for CEQA purposes. Would the project:
A. Substantially alter the existing drainage patterns of the site or area, including through the
alteration if the course of a stream or river, in a manner which would result in substantial
erosion or siltation on -or off-site?
.,. The project does not substantially alter the existing drainage pattern of the area and
does not alter the course of a stream or river. ,. ..
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The storm drain system for the entire project is designed to route and convey all
resulting runoff from developed conditions to existing point of discharge.
B. Substantially alter the existing drainage patterns of the site or area, including through the
alteration of the course of a stream or river, or substantially increase the rate or amount of
surface runoff in a manner which would result in flooding on-or off-site?
The project will not substantially alter the existing drainage pattern of the area as it will
not alter the course of a stream or river, and also will not substantially increase the rate
or amount of surface runoff in a manner which would result in on-or off-site flooding .
C. Create or contribute runoff water which would exceed the capacity of existing or planned
storm water drainage systems?
No. All project discharge points release water at rates less than or equal to existing
conditions .
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Drainage Study
D. Place housing within a JOO-year flood hazard area as mapped on a federal Flood Hazard
Boundary or Flood insurance Rate Map or other flood hazard delineation map, including
County Floodplain Maps? For example; research the foregoing and provide same (to indicate
applicability or not) in the study?
The project does not place any housing within a 100-year flood hazard area.
E. Place within a JOO-year flood hazard area structures which would impede or redirect flood
,,. flows? ...
There are no structures proposed within a 100-year flood hazard area. ,,.
-., F. Expose people or structures to a significant risk of loss, injury or death involving flooding,
including flooding as a result of the failure of a levee or dam on-sit or off-site? ,.. .. NA
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.., 1.6 -References
I"" "County of San Diego Hydrology Manuaf', June 2003 ...
"San Diego County Hydraulic Design Manuaf', September 2014 ,,.
11w "Stormwater Quality Management Plan for Village Walk", April 2018, REC Consultants.
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1. 7 -Declaration of Responsible Charge
THIS PRELIMINARY DRAINAGE STUDY HAS BEEN PREPARED UNDER THE DIRECTION OF
THE FOLLOWING REGISTERED CIVIL ENGINEER. THE REGISTERED ENGINEER ATTESTS TO
THE TECHNICAL INFORMATION CONTAINED HEREIN AND THE ENGINEERING DATA UPON
WHICH RECOMMENDATIONS, CONCLUSIONS, AND DECISIONS ARE BASED.
Luis A. Parra-Rosales R.C.E. 66377
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CHAPTER 2 -METHODOLOGY
2.1 -County of San Diego Design Criteria
San Diego County Hydrology Manual
Date: June 2003
SECTION3
Section:
Page:
RATIONAL METHOD AND MODIFIED RATIONAL METHOD
3.1 TID:RA110NALM1:THOD
3 1 of26
The Rational Method (RM) is a mathematical formula UBed to determine the maxiJD11m
runoff rate from a given rainfall. It bas particular application in umao storm drainage, when:
it is used to estimate peak runoff rates from small urbao and rural watenheds for the design
of storm drains and small drainage structures. The RM is recommended for analyzing the
runoff response from drainage areas up to approximately I square mile in size. It should not
be used in ins1aru:es where there is a junction of independent drainage systems or for
drainage areas greater than approximately I square mile in size. In these inswu:es, the
Modified Rational Method (MRM) should be used for junctioos of independent drainage
systems in wateisheda up to approximately 1 square mile in size (aee Section 3.4); or the
NRCS Hydrologic Method should be used for wateisheda greater than approximately I
square mile in size (see Section 4).
The RM cao be applied using any design storm frequency (e.g., 100-ycar, SO-year, JO-year,
etc.). The local agency determines the design storm frequency that must be used baaed on
the type of project and specific local requirements. A discussion of design storm frequency
is provided in Section 2.3 of this maoual. A procedure bas been developed that converts the
6-hour and 24-hoor precipitation isopluvial map data to an Intensity-Doratioo curve that cao
be used for the rainfall intensity in the RM formula as shown in Figure 3-1. The RM is
applicable to a 6-hoor storm duratioo because the procedure uses Intensity-Duration Dcaign
Charts that are based oo a 6-hoor storm duration.
3.1.1 Rational Method Formula
The RM fonnula estimates the peak rate of runoff at any location in a watenhed as a function
of the drainage area (A), runoff coefticieot (C), and rainfall intensity (I) for a duration equal
to the time of concentration (T,), which is the time required for w-to
3-1
Village Walk
Drainage Study
2.2 -Design Rainfall Determination
2.2.1 -100-Year, 6-Hour Rainfall lsopluvial Map
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Hydrology Manual
• Rainfalllsoplwials
IN Y-Ralafal -• 6 e..n --)
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+N :-:.:=-:::.=;:;.-..:=-
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Village Walk
Drainage Study
2.2.2 -100-Year, 24-Hour Rainfall lsopluvial Map
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·-ga'!ll!'J==~ I ~, I --I I I I . • I I s,.,.,.
SITE LOCATION
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County of San Diego
Hydrology Manual
• Rainfall Isopluvials
IN Year Ralafall Ennl-24 HNn
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Village Walk
Drainage Study
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2.3 -Runoff Coefficient Determination
Son Diep, County Hyd,olosy Manual
Dale: June 2003
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Table3-l
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RUNOFF COEFFICIENTS FOR URBAN AREAS
LandUoe I Runoft"Coeffici-2l "'C"'
SoilType
NRCSEJemm,uo -%IMPER. A B
Undisturbed Natt.sal Terrain (N.....i) PuUWIWt Open Space O" 0.20 0.25
Low Density Peetdendel (lDR) Raidendal. 1.0 DU/A or leu 10 0.27 0.32
Low Dc:mity R ddentfel (lDR) 'tee:1dcmdel 2.0 'DU/A cw lea 20 0.34 0.38
Low Dmaity Poridrntiel (I.DR) :"'eridmtieJ 2.9 DU/A or 1w 25 0.38 0.41
Medium Dimauy Jtmidmtid (MDR) Reridentiel 4.3 DU/A cw leu 30 0.41 0.45
Medium n.sity ;sterdrneiel (MDR) Peridenriel 7 .3 DU/A or leu 40 0.48 0.51
Medium Demity Reeiderdiel (MDR) Roeidmti:1 10.9 DU/A 01" 1-45 0.52 0.54
Medium I>emity Rm' t ld(MDR) Peridenriel 14.S DU/A or 1w 50 o.ss o.sa
Hipo..;ty-.i-tial (IIDR) Reridenfiel 24.0 DU/A or 1-65 0.66 0.67
Hqil, o..ity -.i-tial (IIDR) ~ 43.0 DU/A or•-80 0.76 0.77
~ (N. Com) N-Commen,ial 80 0.76 0.77
~ (G. Com) a-a!C oW 85 0.80 0.80
~(0.P.Com) Office Plof sicnellC oW 90 0.83 0.84
~ (Llmiu,d I.) U..-1'.nduatrial 90 0.83 0.84 ---~ 9.87 o.arr
r I
C
0.30
0.36
0.42
0.4.S
0.-48
0.54
0.57
0.60
0.69
0.78
0.78
0.81
0.84
0.84
0.87
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D
0.35
0.41
0.46
0.49
0.52
0.57
0.60
0.63
0.71
0.79
0.79
0.82
o.as
0.85
0.87
~ vdDes ciatod with 0% impCll'Yioua may be u:aed ftJr dinct celndsti of die nmoff cocfflcicrd • deac:nl,ed in SoctioD 3.1.2 (npnNDtina 1ho pervioua nmotr
coefflcicnt,, ep, fbr tho aoil type). or for__. that will win undisturbod in perpetuity. Justification must be afVCll'I ttw the area will nm,am natural fi:Jftwcr (o.a .• the area
it localed in CleveblDd Natioaal Pormt).
DU/A• ctweUi:na uai&s par acre
NR.CS •Natioaal ~Con 11tic11 'Service
3-6
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Drainage Study
San Diego County Hydrology Mmual
Date: June 2003
Section: Page:
• The storm frequency of peak discharges is the same as that of I for the given T, .
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• The fraction of rainfall that becomes runoff ( or the runoff coefficieot, C) is independeot
of I or precipitation zone number (PZN) condition (PZN Condition is discussed in
Section 4.1.2.4).
• The peak rate of runoff is the only infmmatioo produced by using the RM.
3.1.2 Runoff Coefficient
Table 3-1 lists the estimated runoff coefficients for urban sreas. The concepts related to the
runoff coefficient were evaluated in a report entitled Evaluation. Rationo/ Mefhod '"C""
Values (Hill, 2002) that was reviewed by the Hydrology Manual Committee. The Report ill
available at San Diego County Deportment of Public Works, Flood Control Section and on
the San Diego County Department of Public Works web page.
The runoff coefficients sre based on land use and soil type. Soil type can be determined from
the soil type map provided in Appendix A. An appropriate runoff coefficient (C) for each
type of land use in the subsrea should be selected from this table and multiplied by the
percentage of the total ares (A) included in that class. The sum of the products for all land
uses ill the weighted runoff coefficient (l:[CAJ). Good engineering judgment should be used
when applying the values presented in Table 3-1, as adjustments to these values may be
appropriate based on site-specific characteristics. In any event, the impervious percentage
("lo Impervious) as given in the table, for any area, shall govern the selected value for C. The
runoff coefficient can also be calculated for an ares based on soil type and impervious
percentage using the following formula:
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Drainage Study
Son Di ... County Hydrology Manual
Date: June 2003
Section:
Page:
3 Sof26
C = 0.90 x (%Impervious)+ C,, x (1 -% Impervious)
Where: C,, = Pervious Coefficient Runoff Value for the soil type (shown in
Table 3-1 as Undisturbed Natural Terrain/Permanent Open Space,
0% Impervious). Soil type can be determined from the soil type map
provided in Appendix A.
The values in Table 3-1 are typical for most urban areas. However, if the basin contains rural
or agricultursl land use, parks, golf courses, or other types of nonurban land use that are
expected to be permanen~ the appropriate value should be selected based upon the soil and
cover and approved by the local agency .
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2.4 -Urban Watershed Overland Time of Flow Nomoqraph
San Diego County Hydrology Manual
Date: June 2003
Section:
Page:
3 12of26
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 wi1h an area of two or loss acres does not have
a significant effect whore 1he drainage basin area is 20 to 600 acres.
Table 3-2 provides limita of 1ho length (Maximum Length (LM)) of shoot flow to be used in
hydrology studios. Initial T, values based on average C values for the Land Use Element are
also included. These values cao ho used in planning and design applications as described
below. Exceptions may be approved by 1ho "Regulating Agency" when submitted wi1h a
detailed stody .
Table3-2
MAXIMUM OVERLAND FLOW LENGTH (L.,)
& INITIAL TIME OF CONCENTRATION (T.)
Element• DU/ .5% 1 o/o 2% 3% 5% 10%
Acre 4t T; 4t T, LM T, LM T, LM T, LM T;
Natural so 13.2 70 12.5 85 10.9 100 10.3 100 8.7 100 6.9
IDR 1 50 12.2 70 11.5 85 10.0 100 9.5 100 8.0 100 6.4
IDR 2 so 11.3 70 10.5 85 9.2 100 8.8 100 7.4 100 5.8
IDR 2.9 50 10.7 70 10.0 85 8.8 95 8.1 100 7.0 100 5.6
MDR 4.3 so 10.2 70 9.6 80 8.1 95 7.8 100 6.7 100 5.3
MDR 7.3 so 9.2 65 8.4 80 7.4 95 7.0 100 6.0 100 4.8
MDR 10.9 50 8.7 65 7.9 80 6.9 90 6.4 100 5.7 100 4.5
MDR 14.5 50 8.2 65 7.4 80 6.5 90 6.0 100 5.4 100 4.3
HDR 24 50 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 95 3.4 100 2.7
N.Com 50 5.3 60 4.5 75 4.0 85 3.8 95 3.4 100 2.7
G.Com 50 4.7 60 4.1 75 3.6 85 3.4 90 2.9 100 2.4
O.P./Com 50 4.2 60 3.7 70 3.1 80 2.9 90 2.6 100 2.2
Limited I. 50 4.2 60 3.7 70 3.1 80 2.9 90 2.6 100 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
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~ w ~
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0
EXAMPLE:
Given Watercourse Distance (DJ = 70 Feet
Slope (s) = 1.3%
Runoff Coefficient (C) = 0.41
Overland Ftow Time (T) = lil.5Minlllea
T= 1.8(1.1-C)VD
'V.
SOURCE: Airport Drainage, Federal Aviation Administration, 1965
J<'IGURE
Rational Formula -Overland Time of Flow Nomograph
I 3.3 I
Village Walk
Drainage Study
2.5 -County of San Diego Intensity-Duration Curve
1 1',, 10.0
9.0
8.0
7.1 " ,r--...
r-.J. 6.0 I
5.0
4.
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EQUATION
I = 7.44 Ps D-0-645 I
I = Intensity (in/hr)
I
P 6 = 6-Hour Precipitation (in)
D = Duration (min)
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,,
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5 i; i' ii ii 1·0 f5 20 :io ,o so i
Duration
3
Hours Minutes
I
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I
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5 6
'r' I g
"0 3. 6.0 >!.
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1,5
1.0
Intensity-Duration Design Chart -Template
Dlrec:tlons for Application:
(1) From precipitation maps detennine 6 hr and 24 hr amounts
for the selected frequency. These maps are induded in the
County Hydrology Manual (10. 50, and 100 yr maps included
in the Design and Procedure Manual).
(2) Adjust 6 hr precipitation (if necessary) so that it is within
the range of 45% to 65% of the 24 hr precipitation (not
applicaple to Desert).
(3) Plot 6 hr precipitation on the right side of the chart.
(4) Draw a line through the point parallel to the plotted lines.
(5) This line is the intensity-duration curve for the location
being analyzed.
Application Fonn:
(a) Selected frequency~ year p
(b) Ps = 2L_ in., P24 = _.iL ,..'.:..2..p = 2.L_ %(2)
24
(c) Adjusted p6c2> = __ in.
(d) Ix = __ min.
(e) I = ___ in.Jhr.
Note: This chart replaces the Intensity-Duration-Frequency
curves used since 1965.
P6 1 1.5 2 2.5 3 3.5 4 4.5 5 5.5
'Duration l I I I I I I I I I
5 2.63 3.95 5.27 6.59 7.90 9.22 10.54 1186 13.t7 14.49 15.81
1 2.12 3.18,4.24 5.30_6.36.J.42 a.48 9.54 10.60, 11.66 12.n
10 1.~ 2.53 337_4.21 5.05.~90 6.74 758 8.42 9.27 10,11
1~ 1~_1.95 2.59 3.24 3.89~.54~5.19 5.84_6.49 7.13 ! 7.78
20 1.08 1.62 2.15 2.69 3.23 3.77 4.3_1_ ·~ 5.39 t 5.93 6.46
25 0.93 1.40 1.87 2.33 2.80 3.27 3.73 4.20 4.67 5.13 5.80
: ~:: :~: ::: ~~~ ~: ~:i: ~~ ~:~ ~-.!; ~:~ ::~
50 o.8040.90, 1.19 1.49 1.79 2.09 2.39 2.69 2.98 3.28 3.58
80 0.53 080 1.06 1.33 1 59 1 86 2.12 2.39 2.65 2.92 3 18
90 0 41 0 61 0 82 1.02 1.23 1 43 1.63 1.84 0 2.04 2.25 2.45
120 0.34 0 51 0 68 0 85 1.02 1 19 1.36 1.53 1.70 1.87 2.04
1so o.29 ·o.«!oss o.73 o.88 1.00 1.18 1.32 1.41 1.62 1.16
:: ~ g::r~:~·g:: ~:-{~!-~~ ~:: :~ :-~ :~
300 0.19 0.28 0.38 0•1 0.56 0.66 0.75 0.85 0.94 1.03 1.13
360 0.17 0.2510.33 0.42 0.50'0~58 0.67 0.75 0.84-0.92 1.00
3-1
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Village Walk
Drainage Study
2.6 -Model Development Summary (from County of San Diego Hydrology
Manual)
San Diego County Hydrology Manual
Date: June 2003
3.2 DEVELOPING INPlIT DATA FOR THE RATIONAL METHOD
Section:
Page:
3
20of26
This section describes the development of the neoessary data to perfonn RM calculations.
Section 3.3 describes the RM calculation process. Input data for calculating peak flows and
T,'s with the RM should be developed as follows:
I. On a topographic base map, outline the overall drainage area boundary, showiog
adjacent dlains, existing and proposed dlains, end overland flow paths.
2. Verify the accuracy of the drainage map in the field.
3. Divide the drainage area into subareas by locating significant points of interest. These
divisions should be based on topography, soil type, end land use. Ensure that en
appropriate first subarea is delineated. For natural areas, tho first subarea flow path
length should be loss then or equal to 4,000 feet plus tho overland flow length (Table
3-2). For developed areas, tho initial subarca flow path length should be consistent
with Table 3-2. The topography end slope within the initial subarea should be
generally unifonn.
4. Working from upstream to downstream, assign a number representing each subarea in
the drainage systmn to each point of interest. Figure 3-8 provides guidelines for node
numbers for geographic infollll8tion system (GIS)-based studies.
S. Measure each sub.,.. in the drainage area to detennine its size in acn:s (A) .
6, Detcrmino the length and effective slope of the flow path in each subarea.
7. Identify the soil type for each subarea .
3-20
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'"' 1111
Village Walk
Drainage Study
San Diogo County Hydrology Manual
Date: June 2003
Section:
Page:
3
22of26
8. Determine the runoff eoefficient (C) for each subarea based on Table 3-1. If the
subarea contains more than one type of development classificati~ use a proportionate
average for C. In determining C for the subarea, use future land use taken from the
applicable community plan, Multiple Speciea conservation Plan, National Forest land
use plan, etc •
9. Calculate the CA value for the suharea.
10. Calculate the ~CA) value(s) for the subareas upstream of the point(s) of interest .
1 I. Determine Po and P24 for the study using the isopluvial maps provided in Appeodix B .
If necessary, adjust the value for P6 to be within 45% to 65% of the value for P24 .
See Section 3.3 for a deacription of the RM calculation proceas.
3.3 l'ERFoRMING RATIONAL MEmoo CALCULATIONS
This section describes the RM calculation process. Using the input data, calculation of peak
flows and T ,'s should be performed as follows:
I. Determine T, for the first subarea. Use Table 3-2 or Figure 3-3 as discussed in Section
3.1.4. If the watembed is natural, the travel time to the downstream eod of the first
subarea can be added to T,to obtain theT. Refer to paragraph 3.1.4.2 (a) .
2. Determine I for the subarea using Figure 3-1. If T, was less than 5 minutes, use the 5
minote time to determine intensity for calculatiog the flow.
3. Calculate the peak discharge flow rate for the suharea, where Q,,-~CA) I.
In case that the downstream flow rate is less than the upstream flow rate, due to the
long travel time that is not offset by the additional subarea runoff, use the upatrcam
peak flow for design purposes until downstream flows increase again.
~22
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...
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...
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Village Walk
Drainage Study
Son Diego Cow,fy Hydrology Manual
Date: June 2003
4. Estimate the T1 to the next point of interest
S. Add the Tt to the previous To t.o obtain a new Tc,
Section:
Page:
6. Continue with step 2, above, until the final point of interest is reached.
3
23 of26
Note: The MRM should be used to calculate the peak discharge when there is a junction
from independent subareas into the drainage system.
3.4 MODIFIED RATIONAL METHOD (FOR JtJNCTION ANALYSIS)
The pu,pose of this section is to describe the steps necesaary to develop a hydrology report
for a small watershed using the MRM. It is neceasuy to use the MRM if the wstershed
contains junctions of independent drainage syatems. The process is based on the deaign
manuals of the City/County of San Diego. The general process description for using this
method, including an example of the application of this method. is described below.
The engineer shoold only use the MRM for drainage areas up to approximately I square mile
in size. If the wstershed will significantly exceed I square mile then the NRCS method
described in Section 4 should be used. The engineer msy choose to use either the RM or tho
MRM for calculstions for up to an approximately I-square-mile area and then transition the
study to the NRCS method for additional downstream areas that exceed approximately 1
square mile. The transition process is described in Section 4.
3.4.1 Modlliod Rational Method General Proceo• Description
Tho general process for the MRM differs from the RM only when a juncticm of independent
drainage systems is reached. Tho peak Q, T ~ and I for each of the independent drainage
systems at the point of the junction are calculated by the RM. Tho independent drainage
systems sre then combined using the MRM procedure descnl,ed below. The peak Q, T ~ and
I for each of tho independent drainage systems at tho point of the junction must be calculated
prior to using tho MRM procedure to combine tho independent drainage systems, as these
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Village Walk
Drainage Study
San Di°"" County Hydrology Manual
Date: June 2003
Section:
Page:
3 24of26
values will be used for tho MRM calculations. After the independent dniinage sys1mls have
been combined, RM calculations are continued to tho next point of interest.
3.4.2 Procedure for Combining Independent Drainage S)'lteml at a Junction
Calculate the peak Q, T,, and I for each of the independent drainage systems at the point of
the junction. These values will be used for the MRM calculations .
At the junction of two or more independent dniinage sys1mls, the respective peak flows are
combined to obtain the maximum flow out of the junction at Tc. Based on the approximation
that total runoff increases directly in proportion to time, a general equation may be written to
determine the mi,wnum Q and its corresponding T, using the peak Q, T,, and I for each of
the independent drainage systems at the point inunediately before the junction. The general
equation roquires that contributing Q's be numbenxl in order of increasing T, .
Let Q,, T1, and l1 correspond to the tributary area with the shortest T,. Likewise, let Q,, T2,
and I, correspond to the tributary area with tho next longer T,; Q,, T,, and I, correapond to
the tnlnmuy area with the next longer T,; and so on. When only two independent dniinage
systems are combined, leave Q,, T ,, and I, out of the equation. Combine the independent
dniinage sys1mls using the junction equation below:
Junction Equation: T 1 < T2 < T 3
On-0,+70,+;Q,
' '
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"" ...
"" ...
"" -..
1111 ..
1111 .. ..
'"" ' ..
Village Walk
Drainage Study
San Di ... County Hydrology Manual
Date: June 2003
Section:
Page:
3 25 of26
Calculate Qr1, Qn, and Qn. Select tho largest Q and use the T, associated with that Q for
further calculations (soo tho three Notes for options). If tho largest calculated Q's an: equal
(e.g., Qn = Qn > Qn), use the shorter of tho T,'s associated with thst Q.
This equation may be expanded for a junction of more thso thn:e independent drainage
systems using tho same concept. Tho concept ia thst when Q from a selected subaroa (e.g.,
Q,) is combined with Q from another suban:a with a shorter T, (e.g., Q,), tho Q from the
suban:a with the shorter T, is reduced by the ratio of tho l's (I,/11); and when Q from a
selected suban:a (e.g., Q,) ia combined with Q from another suban:a with a longer T, (e.g.,
Q,), the Q from the subaroa with tho longer T, is mluced by tho ratio of tho To's (T,!r,).
Note #1: At a junction of two independent drainage systems thst have tho same T,. tho
tributary flows may be added to obtain tho Q,.
This can be verified by using tho junction equation above. Let Q,, T,, and I, = 0. When T 1
and T2 are the same, It and 12 are also the same, and T1ff2 and Iv'11 = 1. T1ff2 and 12'11 are
cancelled from tho equations. At this poin~ Qn = Qn = Q, + Q,.
~: In tho upstream part of a watershed, a conservative computation ia acceptable.
When tho times of concentration (To's) ere relatively close in magnitude (within 10%), use
the shorter T, for tho intensity and the equation Q = :E(CA)I .
Note #3: . An optional method of determining tho T, is to use tho equation
T, = [(L (CA)7.44 P,)IQ] 1.5'
This equation ia from Q = l:(CA)I = L{CA)(7.44 Po!T/" ) and solving for T,. The
advantage in this option ia thst the T, ia consistent with tho peak flow Q, and avoids
iDappropriate fluctuation in downstream flows in some cases.
:1-25
..
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Village Walk
Drainage Study
CHAPTER 3 -100 YEAR HYDROLOGIC ANALYSIS FOR
EXISTING CONDITIONS
Ill'
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.. -.. --
-.. -
******************************************~*********************************
RATIONAL METHOD HYDROLOGY COMPUTER PROGRAM PACKAGE
Reference: SAN DIEGO COUNTY FLOOD CONTROL DISTRICT
2003,1985,1981 HYDROLOGY MANUAL
(c) Copyright 1982-2015 Advanced Engineering Software (aes)
Ver. 22.0 Release Date: 07/01/2015 License ID 1643
Analysis prepared by:
************************** DESCRIPTION OF STUDY**************************
* VILLAGE WALK -EXISTING CONDITIONS 100-YEAR ANALYSIS
* WEIGHTED C=0.58 (IMP=8574 SQ.FT, PER=8224 SQ.FT, CLASS B SOIL)
* **************************************************************************
FILE NAME: VWEX100.DAT
TIME/DATE OF STUDY: 09:48 02/12/2018
USER SPECIFIED HYDROLOGY AND HYDRAULIC MODEL INFORMATION:
2003 SAN DIEGO MANUAL CRITERIA
USER SPECIFIED STORM EVENT(YEAR) = 100.00
6-HOUR DURATION PRECIPITATION (INCHES) = 2.600
SPECIFIED MINIMUM PIPE SIZE(INCH) = 18.00
SPECIFIED PERCENT OF GRADIENTS(DECIMAL) TO USE FOR FRICTION SLOPE= 0.95
SAN DIEGO HYDROLOGY MANUAL "C"-VALUES USED FOR RATIONAL METHOD
NOTE: USE MODIFIED RATIONAL METHOD PROCEDURES FOR CONFLUENCE ANALYSIS
*
*
*
*USER-DEFINED STREET-SECTIONS FOR COUPLED PIPEFLOW AND STREETFLOW
HALF-CROWN TO STREET-CROSSFALL: CURB GUTTER-GEOMETRIES:
WIDTH CROSSFALL IN-/ OUT-/PARK-HEIGHT WIDTH LIP HIKE
NO. (FT) (FT) SIDE / SIDE/ WAY (FT) (FT) (FT) (FT)
MODEL*
MANNING
FACTOR
In)
========= ==========--===== ======
1 30.0 20.0 0.018/0.018/0.020 0.67 2.00 0.0313 0.167 0.0150
GLOBAL STREET FLOW-DEPTH CONSTRAINTS:
1. Relative Flow-Depth= 0.00 FEET
as (Maximum Allowable Street Flow Depth) -(Top-of-Curb)
2. (Depth)*(Velocity) Constraint= 6.8 (FT*FT/S)
*SIZE PIPE WITH A FLOW CAPACITY GREATER THAN
OR EQUAL TO THE UPSTREAM TRIBUTARY PIPE.*
****************************************************************************
FLOW PROCESS FROM NODE 1. 00 TO NODE 2.00 IS CODE= 21
>>>>>RATIONAL METHOD INITIAL SUBAREA ANALYSIS<<<<<
==================--==========-----=========--------===---------------------
*USER SPECIFIED(SUBAREA):
USER-SPECIFIED RUNOFF COEFFICIENT= .5800
S.C.S. CURVE NUMBER (AMC II) = 0
INITIAL SUBAREA FLOW-LENGTH(FEET) = 90.00
UPSTREAM ELEVATION(FEET) = 54.41
DOWNSTREAM ELEVATION(FEET) = 51.81
ELEVATION DIFFERENCE(FEET) = 2.60
SUBAREA OVERLAND TIME OF FLOW(MIN.) = 6.196
WARNING: INITIAL SUBAREA FLOW PATH LENGTH IS GREATER THAN
C
11111
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1111
'"' ..
... -
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...
--
THE MAXIMUM OVERLAND FLOW LENGTH= 88.89
(Reference: Table 3-18 of Hydrology Manual)
THE MAXIMUM OVERLAND FLOW LENGTH IS USED IN Tc CALCULATION!
100 YEAR RAINFALL INTENSITY(INCH/HOUR) = 5.965
SUBAREA RUNOFF(CFS) 0.48
TOTAL AREA(ACRES) = 0.14 TOTAL RUNOFF(CFS) 0.48
******************************************~*********************************
FLOW PROCESS FROM NODE 2.00 TO NODE 3.00 IS CODE= 51
----------------------------------------------------------------------------
>>>>>COMPUTE TRAPEZOIDAL CHANNEL FLOW<<<<<
>>>>>TRAVELTIME THRU SUBAREA (EXISTING ELEMENT)<<<<<
====================================================-===========--=========-
ELEVATION DATA: UPSTREAM(FEET) = 51.81 DOWNSTREAM(FEET) 47.87
CHANNEL LENGTH THRU SUBAREA(FEET) = 134.80 CHANNEL SLOPE 0.0292
CHANNEL BASE(FEET) 5.00 "Z" FACTOR= 2.000
MANNING'S FACTOR= 0.035 MAXIMUM DEPTH(FEET) = 1.00
100 YEAR RAINFALL INTENSITY(INCH/HOUR) = 5.227
*USER SPECIFIED(SUBAREA):
USER-SPECIFIED RUNOFF COEFFICIENT= .5800
S.C.S. CURVE NUMBER (AMC II) = 0
TRAVEL TIME COMPUTED USING ESTIMATED FLOW(CFS) 0.86
TRAVEL TIME THRU SUBAREA BASED ON VELOCITY(FEET/SEC.) 1.60
AVERAGE FLOW DEPTH(FEET) 0.10 TRAVEL TIME(MIN.) 1.41
Tc(MIN.) = 7.60
SUBAREA AREA(ACRES) 0.25 SUBAREA RUNOFF(CFS) 0.76
AREA-AVERAGE RUNOFF COEFFICIENT 0.580
TOTAL AREA(ACRES) = 0.4 PEAK FLOW RATE(CFS) 1.18
END OF SUBAREA CHANNEL FLOW HYDRAULICS:
DEPTH(FEET) = 0.13 FLOW VELOCITY(FEET/SEC.)
LONGEST FLOWPATH FROM NODE 1.00 TO NODE
1. 77
3.00 = 224.80 FEET.
============================================================================
END OF STUDY SUMMARY:
TOTAL AREA(ACRES)
PEAK FLOW RATE(CFS)
0. 4 TC (MIN. I =
1. 18
7.60
--=====------=====--------====--------===---------==---------===------------
============================================================================
END OF RATIONAL METHOD ANALYSIS
..
...
1111
... ..
... ..
... ..
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... ..
... ..
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... ... ..
• ,. -.. -... .. -..
Village Walk
Drainage Study
CHAPTER 4 -100 YEAR HYDRO LOGIC ANALYSIS FOR
DEVELOPED CONDITIONS -UNMITIGATED
.. .. .. .. .. ..
'"" ..
'"" .. .. ... .. ... .. ... .. .. ..
,..
... ...
... .. .. ... ----------
****************************************************************************
RATIONAL METHOD HYDROLOGY COMPUTER PROGRAM PACKAGE
Reference: SAN DIEGO COUNTY FLOOD CONTROL DISTRICT
2003,1985,1981 HYDROLOGY MANUAL
(c) Copyright 1982-2015 Advanced Engineering Software (aes)
Ver. 22.0 Release Date: 07/01/2015 License ID 1643
Analysis prepared by:
************************** DESCRIPTION OF STUDY**************************
* VILLAGE WALK -DEVELOPED CONDITIONS 100-YEAR ANALYSIS
* WEIGHTED C=0.72 (IMP=ll701 SQ.FT,, PER=4484 SQ.FT., CLASS B SOIL
**************************************************************************
FILE NAME: C:\AES\VWDEV100.DAT
TIME/DATE OF STUDY: 11:18 05/23/2018
USER SPECIFIED HYDROLOGY AND HYDRAULIC MODEL INFORMATION:
2003 SAN DIEGO MANUAL CRITERIA
USER SPECIFIED STORM EVENT{YEAR) = 100.00
6-HOUR DURATION PRECIPITATION (INCHES) = 2.600
SPECIFIED MINIMUM PIPE SIZE(INCH) = 6.00
SPECIFIED PERCENT OF GRADIENTS(DECIMAL) TO USE FOR FRICTION SLOPE= 0.95
SAN DIEGO HYDROLOGY MANUAL "C"-VALUES USED FOR RATIONAL METHOD
NOTE: USE MODIFIED RATIONAL METHOD PROCEDURES FOR CONFLUENCE ANALYSIS
*USER-DEFINED STREET-SECTIONS FOR COUPLED PIPEFLOW AND STREETFLOW MODEL*
*
*
HALF-CROWN TO STREET-CROSSFALL:
WIDTH CROSS FALL IN-I OUT-/PARK-
NO. (FT) (FT) SIDE I SIDE/ WAY
CURB
HEIGHT
(FT)
GUTTER-GEOMETRIES:
WIDTH LIP HIKE
(FT) (FT) (FT)
MANNING
FACTOR
lnl
========= =================
1 30.0 20.0 0.018/0.018/0.020 0.67 2.00 0.0313
GLOBAL STREET FLOW-DEPTH CONSTRAINTS:
1. Relative Flow-Depth= 0.00 FEET
as (Maximum Allowable Street Flow Depth) -(Top-of-Curb)
2. (Depth)* (Velocity) Constraint = 6.0 (FT*FT/Sl
*SIZE PIPE WITH A FLOW CAPACITY GREATER THAN
OR EQUAL TO THE UPSTREAM TRIBUTARY PIPE.*
0. 167 0.0150
****************************************************************************
FLOW PROCESS FROM NODE 1.00 TO NODE 2.00 IS CODE= 21
----------------------------------------------------------------------------
>>>>>RATIONAL METHOD INITIAL SUBAREA ANALYSIS<<<<<
*USER SPECIFIED{SUBAREA):
USER-SPECIFIED RUNOFF COEFFICIENT .7200
S.C.S. CURVE NUMBER (AMC II) = 0
INITIAL SUBAREA FLOW-LENGTH(FEET) =
UPSTREAM ELEVATION(FEET) = 51.20
DOWNSTREAM ELEVATION(FEET) = 50.60
ELEVATION DIFFERENCE(FEET) = 0.60
SUBAREA OVERLAND TIME OF FLOW(MIN.) =
100 YEAR RAINFALL INTENSITY(INCH/HOUR)
SUBAREA RUNOFF(CFS) 0.52
60.00
5.298
6.599
TOTAL AREA(ACRES) = 0.11 TOTAL RUNOFF(CFS) 0.52
****************************************************************************
FLOW PROCESS FROM NODE 2.00 TO NODE 3.00 IS CODE= 51
----------------------------------------------------------------------------
>>>>>COMPUTE TRAPEZOIDAL CHANNEL FLOW<<<<<
>>>>>TRAVELTIME THRU SUBAREA (EXISTING ELEMENT)<<<<<
I"'
11111
...
11111
..
C
... ..
..
...
... ..
... ...
... ..
... ..
... ..
... -...
1111
1111
...
..
=---------------=-===-------------======----------=========-----=-==========
ELEVATION DATA: UPSTREAM(FEET) = 50.60 DOWNSTREAM{FEET)
CHANNEL LENGTH THRU SUBAREA(FEET) = 183.00 CHANNEL SLOPE
CHANNEL BASE(FEET) 3.00 "Z" FACTOR= 1.000
MANNING'S FACTOR= 0.035 MAXIMUM DEPTH(FEET) = 1.00
100 YEAR RAINFALL INTENSITY(INCH/HOUR) = 5.297
*USER SPECIFIED{SUBAREA):
USER-SPECIFIED RUNOFF COEFFICIENT= .7200
S.C.S. CURVE NUMBER {AMC II) = 0
TRAVEL TIME COMPUTED USING ESTIMATED FLOW(CFS)
TRAVEL TIME THRU SUBAREA BASED ON VELOCITY(FEET/SEC.)
AVERAGE FLOW DEPTH(FEET) 0.22 TRAVEL TIME(MIN.)
1.02
1. 42
2.15
48.77
0.0100
Tc(MIN.) = 7,45
SUBAREA AREA(ACRES) 0. 2 6 SUBAREA RUNOFF(CFS)
0.720
0. 99
AREA-AVERAGE RUNOFF COEFFICIENT
TOTAL AREA(ACRES) = 0.4 PEAK FLOW RATE(CFS) 1. 41
END OF SUBAREA CHANNEL FLOW HYDRAULICS:
DEPTH(FEET) = 0.27 FLOW VELOCITY{FEET/SEC.)
LONGEST FLOWPATH FROM NODE 1.00 TO NODE
1. 60
3.00 = 243.00 FEET.
+--------------------------------------------------------------------------+
ROUTED FLOW FROM HMS MODEL
I C=0.69, A=0.4, Tc=7.45+5=12.45 min, Q=0.8 cfs
I
+--------------------------------------------------------------------------+
****************************************************************************
FLOW PROCESS FROM NODE 3.00 TO NODE 4.00 IS CODE= 7
>>>>>USER SPECIFIED HYDROLOGY INFORMATION AT NODE<<<<<
============================================================================
USER-SPECIFIED VALUES ARE AS FOLLOWS:
TC(MIN) = 12.45 RAIN INTENSITY(INCH/HOUR) = 3.80
TOTAL AREA(ACRES) = 0.40 TOTAL RUNOFF(CFS) = 0.86
****************************************************************************
FLOW PROCESS FROM NODE 3.00 TO NODE 4.00 IS CODE= 31
>>>>>COMPUTE PIPE-FLOW TRAVEL TIME THRO SUBAREA<<<<<
>>>>>USING COMPUTER-ESTIMATED PIPESIZE (NON-PRESSURE FLOW)<<<<<
=-----===============--================================----============-----
ELEVATION DATA: UPSTREAM(FEET) = 45.00 DOWNSTREAM(FEET)
FLOW LENGTH(FEET) = 202.00 MANNING'S N = 0.013
DEPTH OF FLOW IN 9.0 INCH PIPE IS 4.0 INCHES
PIPE-FLOW VELOCITY(FEET/SEC.) 4.53
ESTIMATED PIPE DIAMETER(INCH) = 9.00 NUMBER OF PIPES
PIPE-FLOW(CFS) = 0.86
PIPE TRAVEL TIME(MIN.) = 0.74 Tc(MIN.) =
LONGEST FLOWPATH FROM NODE 1.00 TO NODE
13.19
4.00
41. 55
1
445.00 FEET .
****************************************************************************
FLOW PROCESS FROM NODE 4.00 TO NODE 4.00 IS CODE= 81
>>>>>ADDITION OF SUBAREA TO MAINLINE PEAK FLOW<<<<<
=--------============--=====================================================
100 YEAR RAINFALL INTENSITY(INCH/HOUR) = 3.664
*USER SPECIFIED(SUBAREA):
USER-SPECIFIED RUNOFF COEFFICIENT= .7200
S.C.S. CURVE NUMBER (AMC II) = 0
AREA-AVERAGE RUNOFF COEFFICIENT= 0.5705
SUBAREA AREA{ACRES) 0.01 SUBAREA RUNOFF{CFS)
TOTAL AREA(ACRES) = 0.4 TOTAL RUNOFF(CFS} =
TC{MIN.) = 13.19
0.04
0.87
===----============================================--------==---------------
END OF STUDY SUMMARY:
TOTAL AREA(ACRES)
PEAK FLOW RATE(CFS)
0.4 TC(MIN.) =
0.87
13.19
==--===================------===========--================-=========---~----
--===================----=================================-============---==
END OF RATIONAL METHOD ANALYSIS
,,,. ..
C
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"'" ...
..
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"'" ..
"'" ..
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,,,.
1111
,,,. -,,,. -,,,. ..
Village Walk
Drainage Study
CHAPTER 5 -MODIFIED-PULS DETENTION ROUTING
5.1 -Rational Method Hydrograph
>PYRIGHT 1992, 2001 RICK ENGINEERING COMPANY
,r'ATE 411212018
~OGRAPH FILE NAME Text1
!E OF CONCENTRATION 10 MIN.
~
R RAINFALL 2.6 INCHES
J AREA 0.4 ACRES
t FF COEFFICIENT 0.72
AK DISCHARGE 1.41 CFS
f'(MIN) a 0
"'(MIN) a 10
IE (MIN) a 20
IE (MIN) a 30 t(MIN) a 40
(MIN) a 50
(MIN) a 60
IE (MIN) a 70 t(MIN) a 80
(MIN) a 90
(MIN) a 100
IE(MIN)a 110
,1,;.(MIN) a 120
('"(MIN) a 130
\,,(MIN) a 140
IE (MIN) a 150
IE (MIN) a 160
""'(MIN)a 170
11,,,.(MIN) a 180
ll'l""(MIN) a 190
IE (MIN) a 200
/lia(MIN) a 210
I (MIN) a 220
llloo(MIN) a 230
IE (MIN) a 240
l\f,,(MIN) a 250
r(MIN) a 260
L(MIN) a 270
~(MIN) a 280
IE (MIN) a 290
""'(MIN) a 300
L(MIN) a 310
ll!"'(MIN) a 320
IE (MIN) a 330
,jli,(MIN) a 340
I (MIN) a 350
llloo(MIN) a 360
!E (MIN) a 370 .. ...
.. .. .. -
..
DISCHARGE (CFS) a 0
DISCHARGE (CFS) a 0
DISCHARGE (CFS) a 0
DISCHARGE (CFS) a 0
DISCHARGE (CFS) a 0
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.2
DISCHARGE (CFS) a 0.2
DISCHARGE (CFS) a 0.2
DISCHARGE (CFS) a 1.41
DISCHARGE (CFS) a 0.2
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0.1
DISCHARGE (CFS) a 0
DISCHARGE (CFS) a 0
DISCHARGE (CFS) a 0
~ ..
~ Village Walk .. Drainage Study ..
~
C .. ..
C
"" .. 5.2 -Stage-Storage & Stage-Discharge Relationships ... ..
...
I.
'"" ..
... -... -
"" ..
... ..
~ .. .. -..
i. .. ..
r' ..
Outlet structure for Discharge of Detention Basin 1
Low orifice: 1 "
Number: 0
Cg-low: 0.62
Middle orifice: 1 "
number of orif: 0
Cg-middle: 0.62
invert elev: 0.75 ft
h H/D-low H/D-mid Qlow-orif
(ft) . . (cfs)
0.000 0.000 0.000 0.000
0.100 1.200 0.000 0.000
0.200 2.400 0.000 0.000
0.300 3.600 0.000 0.000
0.400 4.800 0.000 0.000
0.500 6.000 0.000 0.000
0.600 7.200 0.000 0.000
0.700 8.400 0.000 0.000
0.800 9.600 0.600 0.000
0.900 10.800 1.800 0.000
1.000 12.000 3.000 0.000
1.100 13.200 4.200 0.000
1.200 14.400 5.400 0.000
1.300 15.600 6.600 0.000
1.400 16.800 7.800 0.000
1.500 18.000 9.000 0.000
Stage-Storage Calculations
Elev (ft) Area (ft2)
Volume Volume
(ft3) (Ac-ft)
0 440 0 0
0.5 440 220 0.005051
1 440 440 0.010101
1.5 440 660 0.015152
Lower slot
Invert:
B
h
Upper slot
0.00 ft
1.00 ft
0.167 ft
Invert: 0.00 ft
B: 0.00 ft
h O 167 ft
Qlow-weir Qtot-low Qmid-orif
(cfs) (cfs) (cfs)
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
0.000 0.000 0.000
Emergency Weir
Invert:
B:
1.000 ft
8 ft
Qmid-weir Qtot-med Qslot-low
(cfs) (cfs) (cfs)
0.000 0.000 0.000
0.000 0.000 0.098
0.000 0.000 0.277
0.000 0.000 0.380
0.000 0.000 0.459
0.000 0.000 0.527
0.000 0.000 0.586
0.000 0.000 0.641
0.000 0.000 0.691
0.000 0.000 0.737
0.000 0.000 0.781
0.000 0.000 0.823
0.000 0.000 0.862
0.000 0.000 0.900
0.000 0.000 0.936
0.000 0.000 0.971
Qslot-upp Qemer Qtot
(cfs) (cfs) (cfs)
0.000 0.000 0.000
0.000 0.000 0.098
0.000 0.000 0.277
0.000 0.000 0.380
0.000 0.000 0.459
0.000 0.000 0.527
0.000 0.000 0.586
0.000 0.000 0.641
0.000 0.000 0.691
0.000 0.000 0.737
0.000 0.000 0.781
0.000 0.784 1.607
0.000 2.218 3.080
0.000 4.075 4.975
0.000 6.274 7.210
0.000 8.768 9.739
Village Walk
Drainage Study
5.3 -HEC-HMS Modified-Puls Routing Results
Project: VW Simulation Run: 0100
Reservoir: Reservoir-1
Start of Run: 01Jan2000, 00:00 Basin Model: 0100
End of Run: 01Jan2000, 07:00 Meteorologic Model: Met 1
Compute Time: 12Apr2018, 14:06:41 Control Specifications: Control 1
Volume Units:IN
Computed Results
Peak Inflow: 1.410 (CFS)
Peak Discharge: 0.855 (CFS)
Inflow Volume: n/a
Discharge Volumen/a
Date/Time of Peak Inflow: 01Jan2000, 04:10
Date/Time of Peak Discharge01Jan2000, 04: 15
Peak Storage: 0.0 (AC-Fr)
Peak Elevation: 1.009 (Fr)
Reservoir "Reservoir-1" Results for Run "0100"
0.012
0.010
0.008
[ 0.006
! 0.004
0.002
1.6
1.4
1.2
1.0
0.8
i I 0.6
0.4
0.2
0.0
00:00 01:00 02:00
I
Run:Q100 Element:Reservoir-1 Result:Storage
-Run:Q100 Element:Reservoir-1 Result:Outflow
03:00
/
04:00 05:00 06:00
Run:Q100 Element:Reservoir-1 Result:Pool Elevation
---Run:Q100 Element:Reservoir-1 Result:Combined Inflow
1.20
1.00
0.80
o.60 I
0.40
0.20
07:00
01Jan2000
..
Ill ..
1111
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...
i..
...
""
.. .. .. ..
... ..
"" .. .. .. .. ..
,,. ..
"" ..
"" ..
Project: VW Simulation Run: Q100
Reservoir: Reservoir-1
Start of Run: 01Jan2000, 00:00
End of Run: 01Jan2000, 07:00
Compute Time: 12Apr2018, 14:06:41
Date Time Inflow
(CFS)
01Jan2000 00:00 0.000
01Jan2000 00:01 0.004
01Jan2000 00:02 0.008
01Jan2000 00:03 0.012
01Jan2000 00:04 0.016
01Jan2000 00:05 0.020
01Jan2000 00:06 0.024
01Jan2000 00:07 0.028
01Jan2000 00:08 0.032
01Jan2000 00:09 0.036
01Jan2000 00:10 0.040
01Jan2000 00:11 0.040
01Jan2000 00:12 0.040
01Jan2000 00:13 0.040
01Jan2000 00:14 0.040
01Jan2000 00:15 0.040
01Jan2000 00:16 0.040
01Jan2000 00:17 0.040
01Jan2000 00:18 0.040
01Jan2000 00:19 0.040
01Jan2000 00:20 0.040
01Jan2000 00:21 0.041
01Jan2000 00:22 0.042
01Jan2000 00:23 0.043
01Jan2000 00:24 0.044
01Jan2000 00:25 0.045
Basin Model: 0100
Meteorologic Model: Met 1
Control Specifications:Control 1
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.001 0.001
0.0 0.002 0.002
0.0 0.004 0.004
0.0 0.006 0.005
0.0 0.008 0.007
0.0 0.010 0.010
0.0 0.013 0.012
0.0 0.015 0.015
0.0 0.018 0.018
0.0 0.021 0.021
0.0 0.024 0.023
0.0 0.026 0.025
0.0 0.028 0.027
0.0 0.029 0.029
0.0 0.031 0.030
0.0 0.032 0.031
0.0 0.033 0.032
0.0 0.034 0.033
0.0 0.035 0.034
0.0 0.036 0.035
0.0 0.037 0.036
0.0 0.037 0.037
0.0 0.038 0.038
0.0 0.039 0.038
Page 1
Ill
11111
Ill .. ..
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C .. -... ... ..
..
.. -... -... -.. ... ..
Ill
Ill
Ill .. -
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
00:26 0.046
00:27 0.047
00:28 0.048
00:29 0.049
00:30 0.050
00:31 0.050
00:32 0.050
00:33 0.050
00:34 0.050
00:35 0.050
00:36 0.050
00:37 0.050
00:38 0.050
00:39 0.050
00:40 0.050
00:41 0.050
00:42 0.050
00:43 0.050
00:44 0.050
00:45 0.050
00:46 0.050
00:47 0.050
00:48 0.050
00:49 0.050
00:50 0.050
00:51 0.050
00:52 0.050
00:53 0.050
00:54 0.050
00:55 0.050
00:56 0.050
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.040 0.039
0.0 0.041 0.040
0.0 0.042 0.041
0.0 0.043 0.042
0.0 0.044 0.043
0.0 0.045 0.044
0.0 0.046 0.045
0.0 0.046 0.045
0.0 0.047 0.046
0.0 0.047 0.046
0.0 0.048 0.047
0.0 0.048 0.047
0.0 0.049 0.048
0.0 0.049 0.048
0.0 0.049 0.048
0.0 0.049 0.048
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
Page 2
..
1111
"" ' II -..
""
...
"" ..
...
"" ..
"" ..
"" .. -.. .. ..
"' .. -.. -..
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
00:57 0.050
00:58 0.050
00:59 0.050
01:00 0.050
01 :01 0.050
01:02 0.050
01:03 0.050
01:04 0.050
01:05 0.050
01:06 0.050
01:07 0.050
01:08 0.050
01:09 0.050
01 :10 0.050
01 :11 0.050
01:12 0.050
01:13 0.050
01:14 0.050
01 :15 0.050
01:16 0.050
01:17 0.050
01:18 0.050
01:19 0.050
01:20 0.050
01:21 0.051
01:22 0.052
01:23 0.053
01:24 0.054
01:25 0.055
01:26 0.056
01:27 0.057
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.053 0.052
0.0 0.054 0.052
Page 3
"" I .. .. .. .. ..
...
...
... ..
... ..
... .. -.. -...
... ... ..
Ill -• -• ---
""
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
01:28 0.058
01:29 0.059
01:30 0.060
01:31 0.060
01:32 0.060
01:33 0.060
01:34 0.060
01:35 0.060
01:36 0.060
01:37 0.060
01:38 0.060
01:39 0.060
01:40 0.060
01:41 0.060
01:42 0.060
01:43 0.060
01:44 0.060
01:45 0.060
01:46 0.060
01:47 0.060
01:48 0.060
01:49 0.060
01:50 0.060
01:51 0.060
01:52 0.060
01:53 0.060
01:54 0.060
01:55 0.060
01:56 0.060
01:57 0.060
01:58 0.060
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.054 0.053
0.0 0.055 0.054
0.0 0.056 0.054
0.0 0.056 0.055
0.0 0.057 0.056
0.0 0.057 0.056
0.0 0.058 0.057
0.0 0.058 0.057
0.0 0.059 0.058
0.0 0.059 0.058
0.0 0.059 0.058
0.0 0.060 0.058
0.0 0.060 0.059
0.0 0.060 0.059
0.0 0.060 0.059
0.0 0.060 0.059
0.0 0.060 0.059
0.0 0.060 0.059
0.0 0.061 0.059
0.0 0.061 0.059
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
0.0 0.061 0.060
Page 4
... -... -... ..
... -.. ----... -... --... -... ...
---... -..
... ----11111
... ..
... -
Date Time
01Jan2000 01:59
01Jan2000 02:00
01Jan2000 02:01
01Jan2000 02:02
01Jan2000 02:03
01Jan2000 02:04
01Jan2000 02:05
01Jan2000 02:06
01Jan2000 02:07
01Jan2000 02:08
01Jan2000 02:09
01Jan2000 02:10
01Jan2000 02:11
01Jan2000 02:12
01Jan2000 02:13
01Jan2000 02:14
01Jan2000 02:15
01Jan2000 02:16
01Jan2000 02:17
01Jan2000 02:18
01Jan2000 02:19
01Jan2000 02:20
01Jan2000 02:21
01Jan2000 02:22
01Jan2000 02:23
01Jan2000 02:24
01Jan2000 02:25
01Jan2000 02:26
01Jan2000 02:27
01Jan2000 02:28
01Jan2000 02:29
Inflow Storage Elevation Outflow
(CFS) (AC-FT) (FT) (CFS)
0.060 0.0 0.061 0.060
0.060 0.0 0.061 0.060
0.061 0.0 0.061 0.060
0.062 0.0 0.061 0.060
0.063 0.0 0.062 0.060
0.064 0.0 0.062 0.061
0.065 0.0 0.063 0.061
0.066 0.0 0.063 0.062
0.067 0.0 0.064 0.062
0.068 0.0 0.064 0.063
0.069 0.0 0.065 0.064
0.070 0.0 0.066 0.064
0.070 0.0 0.066 0.065
0.070 0.0 0.067 0.066
0.070 0.0 0.068 0.066
0.070 0.0 0.068 0.067
0.070 0.0 0.069 0.067
0.070 0.0 0.069 0.068
0.070 0.0 0.069 0.068
0.070 0.0 0.069 0.068
0.070 0.0 0.070 0.068
0.070 0.0 0.070 0.069
0.071 0.0 0.070 0.069
0.072 0.0 0.071 0.069
0.073 0.0 0.071 0.070
0.074 0.0 0.071 0.070
0.075 0.0 0.072 0.071
0.076 0.0 0.073 0.071
0.077 0.0 0.073 0.072
0.078 0.0 0.074 0.073
0.079 0.0 0.075 0.073
Page 5
---.. ..
1111 ---1111 -.. .. -.. ...
.. .. .. .. ..
,.. ...
... .. .. ... -.. -.. -.. .. ..
Date Time
01Jan2000 02:30
01Jan2000 02:31
01Jan2000 02:32
01Jan2000 02:33
01Jan2000 02:34
01Jan2000 02:35
01Jan2000 02:36
01Jan2000 02:37
01Jan2000 02:38
01Jan2000 02:39
01Jan2000 02:40
01Jan2000 02:41
01Jan2000 02:42
01Jan2000 02:43
01Jan2000 02:44
01Jan2000 02:45
01Jan2000 02:46
01Jan2000 02:47
01Jan2000 02:48
01Jan2000 02:49
01Jan2000 02:50
01Jan2000 02:51
01Jan2000 02:52
01Jan2000 02:53
01Jan2000 02:54
01Jan2000 02:55
01Jan2000 02:56
01Jan2000 02:57
01Jan2000 02:58
01Jan2000 02:59
01Jan2000 03:00
Inflow Storage Elevation Outflow
(CFS) (AC-FT) (FT) (CFS)
0.080 0.0 0.076 0.074
0.080 0.0 0.076 0.075
0.080 0.0 0.077 0.075
0.080 0.0 0.078 0.076
0.080 0.0 0.078 0.077
0.080 0.0 0.079 0.077
0.080 0.0 0.079 0.077
0.080 0.0 0.079 0.078
0.080 0.0 0.080 0.078
0.080 0.0 0.080 0.078
0.080 0.0 0.080 0.078
0.081 0.0 0.080 0.079
0.082 0.0 0.081 0.079
0.083 0.0 0.081 0.079
0.084 0.0 0.082 0.080
0.085 0.0 0.082 0.081
0.086 0.0 0.083 0.081
0.087 0.0 0.084 0.082
0.088 0.0 0.084 0.083
0.089 0.0 0.085 0.083
0.090 0.0 0.086 0.084
0.090 0.0 0.087 0.085
0.090 0.0 0.087 0.085
0.090 0.0 0.088 0.086
0.090 0.0 0.088 0.087
0.090 0.0 0.089 0.087
0.090 0.0 0.089 0.087
0.090 0.0 0.089 0.088
0.090 0.0 0.090 0.088
0.090 0.0 0.090 0.088
0.090 0.0 0.090 0.088
Page6
C ..
..
ill ..
1111 ..
' ..
!"" ..
..
.. -..
... -... ..
.... .. -.. .. ..
"" •
""
1111
... -... -.. ..
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
03:01 0.092
03:02 0.094
03:03 0.096
03:04 0.098
03:05 0.100
03:06 0.102
03:07 0.104
03:08 0.106
03:09 0.108
03:10 0.110
03:11 0.111
03:12 0.112
03:13 0.113
03:14 0.114
03:15 0.115
03:16 0.116
03:17 0.117
03:18 0.118
03:19 0.119
03:20 0.120
03:21 0.122
03:22 0.124
03:23 0.126
03:24 0.128
03:25 0.130
03:26 0.132
03:27 0.134
03:28 0.136
03:29 0.138
03:30 0.140
03:31 0.142
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.091 0.089
0.0 0.091 0.089
0.0 0.092 0.090
0.0 0.093 0.091
0.0 0.094 0.092
0.0 0.095 0.093
0.0 0.096 0.094
0.0 0.098 0.096
0.0 0.099 0.097
0.0 0.101 0.099
0.0 0.102 0.101
0.0 0.103 0.104
0.0 0.104 0.106
0.0 0.105 0.107
0.0 0.106 0.109
0.0 0.107 0.110
0.0 0.108 0.112
0.0 0.108 0.113
0.0 0.109 0.114
0.0 0.110 0.115
0.0 0.110 0.117
0.0 0.111 0.118
0.0 0.112 0.119
0.0 0.113 0.121
0.0 0.114 0.123
0.0 0.115 0.125
0.0 0.116 0.126
0.0 0.117 0.128
0.0 0.118 0.130
0.0 0.119 0.132
0.0 0.120 0.134
Page 7
"'" ..
""' ' -..
"'" 11111
""' ..
I"' ..
.. ...
... ... .. ... ..
"" .. .. .. .. ..
"" ..
"" ---.. .. .. -.. -
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
03:32 0.144
03:33 0.146
03:34 0.148
03:35 0.150
03:36 0.152
03:37 0.154
03:38 0.156
03:39 0.158
03:40 0.160
03:41 0.168
03:42 0.176
03:43 0.184
03:44 0.192
03:45 0.200
03:46 0.208
03:47 0.216
03:48 0.224
03:49 0.232
03:50 0.240
03:51 0.250
03:52 0.260
03:53 0.270
03:54 0.280
03:55 0.290
03:56 0.300
03:57 0.310
03:58 0.320
03:59 0.330
04:00 0.340
04:01 0.447
04:02 0.554
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.121 0.136
0.0 0.122 0.138
0.0 0.123 0.140
0.0 0.125 0.142
0.0 0.126 0.144
0.0 0.127 0.146
0.0 0.128 0.148
0.0 0.129 0.150
0.0 0.130 0.152
0.0 0.132 0.154
0.0 0.134 0.158
0.0 0.136 0.163
0.0 0.139 0.168
0.0 0.143 0.174
0.0 0.146 0.181
0.0 0.150 0.188
0.0 0.154 0.195
0.0 0.158 0.202
0.0 0.162 0.209
0.0 0.167 0.217
0.0 0.171 0.225
0.0 0.176 0.234
0.0 0.181 0.243
0.0 0.186 0.252
0.0 0.191 0.261
0.0 0.197 0.271
0.0 0.202 0.279
0.0 0.208 0.285
0.0 0.214 0.292
0.0 0.227 0.305
0.0 0.252 0.331
Page 8
-..
-•
1111"
1111 -.. .. .. -
,..
11111 -..
,..
11111
,.. .. -...
,..
11111 -11111 -1111 .. .. -11111
,.. ..
,.. ..
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
04:03 0.661
04:04 0.768
04:05 0.875
04:06 0.982
04:07 1.089
04:08 1.196
04:09 1.303
04:10 1.410
04:11 1.288
04:12 1.166
04:13 1.044
04:14 0.922
04:15 0.800
04:16 0.678
04:17 0.556
04:18 0.434
04:19 0.312
04:20 0.190
04:21 0.184
04:22 0.178
04:23 0.172
04:24 0.166
04:25 0.160
04:26 0.154
04:27 0.148
04:28 0.142
04:29 0.136
04:30 0.130
04:31 0.127
04:32 0.124
04:33 0.121
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.287 0.367
0.0 0.332 0.405
0.0 0.386 0.448
0.0 0.449 0.492
0.0 0.519 0.539
0.0 0.599 0.585
0.0 0.686 0.633
0.0 0.781 0.682
0.0 0.869 0.723
0.0 0.936 0.753
0.0 0.983 0.773
0.0 1.007 0.839
0.0 1.009 0.855
0.0 0.998 0.780
0.0 0.977 0.771
0.0 0.940 0.755
0.0 0.890 0.732
0.0 0.826 0.703
0.0 0.758 0.670
0.0 0.693 0.637
0.0 0.633 0.604
0.0 0.575 0.572
0.0 0.522 0.540
0.0 0.472 0.508
0.0 0.425 0.476
0.0 0.382 0.445
0.0 0.343 0.414
0.0 0.306 0.385
0.0 0.274 0.353
0.0 0.245 0.323
0.0 0.219 0.297
Page 9
-.. .. .. .. .. -..
... ..
"" ..
,,,. ..
... .. .. ..
... .. .. .. -..
.. .. ..
.. ..
...
... ..
... ..
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
04:34 0.118
04:35 0.115
04:36 0.112
04:37 0.109
04:38 0.106
04:39 0.103
04:40 0.100
04:41 0.098
04:42 0.096
04:43 0.094
04:44 0.092
04:45 0.090
04:46 0.088
04:47 0.086
04:48 0.084
04:49 0.082
04:50 0.080
04:51 0.079
04:52 0.078
04:53 0.077
04:54 0.076
04:55 0.075
04:56 0.074
04:57 0.073
04:58 0.072
04:59 0.071
05:00 0.070
05:01 0.070
05:02 0.070
05:03 0.070
05:04 0.070
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.197 0.271
0.0 0.178 0.237
0.0 0.163 0.210
0.0 0.151 0.189
0.0 0.141 0.171
0.0 0.133 0.157
0.0 0.126 0.145
0.0 0.120 0.135
0.0 0.116 0.126
0.0 0.112 0.120
0.0 0.109 0.114
0.0 0.106 0.109
0.0 0.104 0.105
0.0 0.102 0.101
0.0 0.100 0.098
0.0 0.098 0.096
0.0 0.096 0.094
0.0 0.094 0.092
0.0 0.092 0.090
0.0 0.091 0.089
0.0 0.089 0.087
0.0 0.088 0.086
0.0 0.086 0.084
0.0 0.085 0.083
0.0 0.083 0.082
0.0 0.082 0.080
0.0 0.081 0.079
0.0 0.080 0.078
0.0 0.079 0.077
0.0 0.078 0.076
0.0 0.077 0.075
Page 10
-.. -..
... --... .. ..
,..
, ..
,.. .. -..
,.. .. .. .. .. .. .. .. -1111 -..
.. .. ..
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
05:05 0.070
05:06 0.070
05:07 0.070
05:08 0.070
05:09 0.070
05:10 0.070
05:11 0.069
05:12 0.068
05:13 0.067
05:14 0.066
05:15 0.065
05:16 0.064
05:17 0.063
05:18 0.062
05:19 0.061
05:20 0.060
05:21 0.059
05:22 0.058
05:23 0.057
05:24 0.056
05:25 0.055
05:26 0.054
05:27 0.053
05:28 0.052
05:29 0.051
05:30 0.050
05:31 0.050
05:32 0.050
05:33 0.050
05:34 0.050
05:35 0.050
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.076 0.075
0.0 0.076 0.074
0.0 0.075 0.074
0.0 0.075 0.073
0.0 0.074 0.073
0.0 0.074 0.072
0.0 0.074 0.072
0.0 0.073 0.072
0.0 0.073 0.071
0.0 0.072 0.071
0.0 0.071 0.070
0.0 0.071 0.069
0.0 0.070 0.068
0.0 0.069 0.068
0.0 0.068 0.067
0.0 0.067 0.066
0.0 0.067 0.065
0.0 0.066 0.064
0.0 0.065 0.064
0.0 0.064 0.063
0.0 0.063 0.062
0.0 0.062 0.061
0.0 0.061 0.060
0.0 0.060 0.059
0.0 0.059 0.058
0.0 0.058 0.057
0.0 0.057 0.056
0.0 0.057 0.055
0.0 0.056 0.055
0.0 0.055 0.054
0.0 0.055 0.054
Page 11
..
1111
,..
Ill
,.. ...
...
""' ...
"" ...
""' ..
"'" ... .. -
""' .. ..
.. ...
""'
""' ...
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
05:36 0.050
05:37 0.050
05:38 0.050
05:39 0.050
05:40 0.050
05:41 0.050
05:42 0.050
05:43 0.050
05:44 0.050
05:45 0.050
05:46 0.050
05:47 0.050
05:48 0.050
05:49 0.050
05:50 0.050
05:51 0.049
05:52 0.048
05:53 0.047
05:54 0.046
05:55 0.045
05:56 0.044
05:57 0.043
05:58 0.042
05:59 0.041
06:00 0.040
06:01 0.036
06:02 0.032
06:03 0.028
06:04 0.024
06:05 0.020
06:06 0.016
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.054 0.053
0.0 0.054 0.053
0.0 0.054 0.052
0.0 0.053 0.052
0.0 0.053 0.052
0.0 0.053 0.052
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.051
0.0 0.052 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.051 0.050
0.0 0.050 0.049
0.0 0.050 0.049
0.0 0.049 0.048
0.0 0.049 0.048
0.0 0.048 0.047
0.0 0.047 0.046
0.0 0.047 0.046
0.0 0.046 0.045
0.0 0.044 0.043
0.0 0.043 0.042
0.0 0.041 0.040
0.0 0.038 0.037
0.0 0.036 0.035
Page 12
..
... ..
,,.
1111 ..
,..
' -,.. ...
... .. -
... --
-.. ..
... .. .. ...
,,. ... .. ...
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
06:07 0.012
06:08 0.008
06:09 0.004
06:10 0.000
06:11 0.000
06:12 0.000
06:13 0.000
06:14 0.000
06:15 0.000
06:16 0.000
06:17 0.000
06:18 0.000
06:19 0.000
06:20 0.000
06:21 0.000
06:22 0.000
06:23 0.000
06:24 0.000
06:25 0.000
06:26 0.000
06:27 0.000
06:28 0.000
06:29 0.000
06:30 0.000
06:31 0.000
06:32 0.000
06:33 0.000
06:34 0.000
06:35 0.000
06:36 0.000
06:37 0.000
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.033 0.032
0.0 0.030 0.030
0.0 0.027 0.027
0.0 0.024 0.024
0.0 0.021 0.021
0.0 0.018 0.018
0.0 0.016 0.016
0.0 0.014 0.014
0.0 0.012 0.012
0.0 0.011 0.011
0.0 0.009 0.009
0.0 0.008 0.008
0.0 0.007 0.007
0.0 0.006 0.006
0.0 0.006 0.005
0.0 0.005 0.005
0.0 0.004 0.004
0.0 0.004 0.004
0.0 0.003 0.003
0.0 0.003 0.003
0.0 0.002 0.002
0.0 0.002 0.002
0.0 0.002 0.002
0.0 0.002 0.002
0.0 0.001 0.001
0.0 0.001 0.001
0.0 0.001 0.001
0.0 0.001 0.001
0.0 0.001 0.001
0.0 0.001 0.001
0.0 0.001 0.001
Page 13
"" ..
,,.. -
"" i ...
"" ..
"" .. .. -.. ..
... .. .. ..
,...
.. .. .. .. .. ... -..
...
.. ..
Date
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
01Jan2000
Time Inflow
(CFS)
06:38 0.000
06:39 0.000
06:40 0.000
06:41 0.000
06:42 0.000
06:43 0.000
06:44 0.000
06:45 0.000
06:46 0.000
06:47 0.000
06:48 0.000
06:49 0.000
06:50 0.000
06:51 0.000
06:52 0.000
06:53 0.000
06:54 0.000
06:55 0.000
06:56 0.000
06:57 0.000
06:58 0.000
06:59 0.000
07:00 0.000
Storage Elevation Outflow
(AC-FT) (FT) (CFS)
0.0 0.001 0.001
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
0.0 0.000 0.000
Page 14
,,.
'111
...
Ill
""' ..
II"' ..
...
...
I"" ..
I""
11111
,.. ..
,..
...
Ila
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,.. -.. ..
,,. ..
Village Walk
Drainage Study
CHAPTER 6 -WSPG HYDRAULIC ANALYSIS
r 1 f 1 f 1 ,-I ,-1
*************************************
Water Surface Profile Gradient (WSPG)
XP WSPG
Engine Version 1.3 06/09/2010
XP Software www.xpsoftware.com
*************************************
INPUT FILE
*************************************
C:\XPS\wspg2010\Samples\DE.wsx
Computed 04/12/18 14:32:54
TITLE INFORMATION
*************************************
WARNING SUMMARY
*************************************
RESULTS
*************************************
f I f J r 1
-------------------==================-------------------------
Main Line ---------------------------------=----------------------------
Composite Profile:
ELEMENT TYPE STATION INVERT GROUND w.s. DEPTH
NAME ELEV ELEV ELEV
f 1 f I ,-I f I ' 1 f I I I ' 1 f I ' -i ir-1
Q VELOC. VELOC. ENERGY SUPER CRITICAL FROUDE SLOPE NORMAL CROSS
HEAD GRADE LN ELEV DEPTH NUMBER DEPTH SECTION
----------------------------------------------------------------------------------------------------
II#
"Node2" Outlet 0.00 41. 66 4 5. 00 43.050 1. 390 0.90 2.58 0.10
HYDRAULIC JUMP at 44.05 of length 0.01
"i .p." 41.10 42.61 45.95 43.277 0.667 0.90 2.58 0.10
"i .p." 43. 97 42. 68 4 6. 02 43.282 0.605 0.90 2.70 0 .11
"i .p." 44.05 42.68 4 6. 02 43.281 0.603 0. 90 2.71 0 .11
"i .p. tt 44.05 42.68 4 6. 02 43.008 0. 32 9 0. 90 5.24 0.43
"i .p. It 172.01 45.64 4 8. 98 45.966 0.329 0.90 5.24 0.43
"i .p." 191.05 4 6. 08 49.42 46.417 0.340 0.90 5.03 0.39
"i .p." 197.45 46.23 49.57 46.578 0.353 0.90 4.80 0.36
"i .p." 200.65 46.30 4 9. 64 46.666 0.366 0.90 4.58 0.33
"i .p. 11 202.54 46.34 4 9. 68 46.724 0.381 0.90 4.36 0.30
"i .p. tt 203.74 46.37 49. 71 46.767 0. 396 0.90 4.16 0. 27
"i .p." 204.46 46.39 4 9. 73 46.800 0. 413 0.90 3. 97 0.24
"i .p." 204.86 4 6. 4 0 4 9. 74 46.827 0.430 0. 90 3.78 0.22
"Linkl" Reach 205.00 4 6. 4 0 48.20 46.848 0.448 0. 90 3.61 0.20
"Nadel" Headwrk 205.00 46.40 48.20 46.849 0.449 0. 90 3.60 0.20
*} in the W.S.ELEV column indicates flooding, it is set whenever W.S.ELEV > GROUND ELEV
i.p. = intermediate point processing results for reaches
43.15 0.000 0.449 0.000 0.00000 0.000 Pipe
43.38 0.000 0. 44 9 0.098 0.02312 0.329 Pipe
43.40 0.000 0.449 0.513 0.02312 0.329 Pipe
43.40 0.000 0.449 0.519 0.02312 0.329 Pipe
43.43 0.000 0.449 1. 818 0.02312 0.329 Pipe
46.39 0.000 0.449 1. 818 0.02312 0.329 Pipe
46.81 0.000 0.449 1. 713 0.02312 0.329 Pipe
46. 94 0.000 0.449 1. 594 0.02312 0.329 Pipe
46.99 0.000 0.449 1. 481 0.02312 0.329 Pipe
47.02 0.000 0.449 l. 375 0.02312 0.329 Pipe
47.04 0.000 0.449 1. 275 0.02312 0.329 Pipe
47.04 0.000 0.449 1.181 0.02312 0.329 Pipe
47.05 0.000 0.449 1.092 0.02312 0.329 Pipe
47.05 0.000 0.449 1. 007 0.02312 0.329 Pipe
47.05 0.000 0.449 0.000 0.00000 0.000 Pipe
.. ...
II"' Village Walk
Drainage Study -
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LEGEND
HYDROLOGY BOUNDARI ES
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