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HomeMy WebLinkAboutDrainage Report
STORMWATER TECHNICAL
REPORT
For:
Culver’s – Carmel
Address:
431 East Carmel Drive, Carmel, IN 46032
Project #W220058
Prepared For:
Meyer Foods Management Company
1448 Conner Street
Noblesville, IN 46060
Phone: (317) 770-4656
Contact: Bob Goins
Prepared By: Daric E. Gordon, E.I.T.
Checked By: Steven S. Rucker, P.E.
Certified By: Steven S. Rucker, P.E.
Date:
February 25, 2022
Revised:
April 29, 2022
August 12, 2022
October 19, 2022
Culver’s – Carmel Weihe Engineers, Inc.
Stormwater Technical Report October 19, 2022
Culver’s - Carmel
431 East Carmel Drive
Carmel, IN 46032
Hamilton County
HYDROLOGY & HYDRAULIC ANALYSIS AND REPORT
PROFESSIONAL CERTIFICATION
___________________________
Steven Scott Rucker, P.E.
Indiana Registration No. PE11300279
The following report and accompanying computations have been developed by me or
under my direct supervision.
Culver’s – Carmel Weihe Engineers, Inc.
Stormwater Technical Report August 12, 2022
TABLE OF CONTENTS
1. Project Narrative
a. Site Background
b. Existing Conditions
c. Proposed Conditions
d. Storm Sewers
e. Water Quality
f. Project Location Map
g. Site Aerial
2. Existing Drainage Calculations
a. Basin Map
b. Runoff Coefficient & Curve Number
c. Hydraflow Hydrographs Analysis
3. Proposed Drainage Calculations
a. Basin Map
b. Runoff Coefficient & Curve Number
c. Hydraflow Hydrographs Analysis
d. Proposed Drainage Details
4. Storm Sewer Calculations
a. Subbasin Map
b. Subbasin Runoff Coefficients
c. Hydraflow Storm Sewer Analysis
5. Water Quality Calculations
a. Location Map
b. Stormwater Quality Calculations
c. Stormwater Quality Unit Selection
d. Stormwater Quality Unit Detail
e. Diversion Structure Detail
f. Dandy Bag Detail & Specifications
6. Appendix
a. FEMA FIRM Map
b. SCS Soil Data for Site Area
c. Carmel STSM Hydrology Standards
d. Proof of Errors and Omissions Insurance
SECTION 1:
PROJECT NARRATIVE
Culver’s – Carmel Weihe Engineers, Inc.
Stormwater Technical Report August 12, 2022
Stormwater Technical Report
Culver’s
431 East Carmel Drive
Carmel, IN 46032
Project W22.0058
Site Background:
Meyer Foods Management Company is proposing to construct a new Culver’s restaurant
on approximately 1.16 acres, located at 431 East Carmel Drive, Carmel, IN 46032,
Indiana. Currently the site is a vacant carwash with, existing structures, pavement,
depressional storage, storm sewers, and utility lines.
The proposed construction is on a site at a Latitude of 39° 57’ 42” N and Longitude of
86° 07’ 08” W, falling within Clay Township. The site is part of the Southwest Quarter of
Section 31, Township 18 North, Range 4 East, Hamilton County, Indiana. Please refer to
Figure 1 as a project location map and Figure 1.1 as a site aerial.
Floodzone:
Based upon a scaled interpretation of the Federal Emergency Management Agency
(FEMA), Flood Insurance Rate Map, Map No. 18057C0228G for Hamilton County,
Indiana, effective date November 19, 2014, the subject tract (commercial development) is
located within Zone X. Zone X refers to minimal risk areas outside the 1-percent and 0.2
percent-annual-chance floodplains. The nearest flood system is Carmel Creek located
approximately 2550-feet to the southwest of the project site. Please refer to the National
Flood Hazard Layer FIRMette attached.
Existing Drainage:
Currently, the project site is a vacant carwash that uses pavement grading and storm
sewers to capture and release storm runoff at a controlled rate using a dry detention pond
as depressional storage. Figure 2 highlights the site’s drainage pattern as four catch
basins capturing an area of 1.03-acres with a curve number of 88.1, leaving a direct
discharge area of 0.13-acres with a curve number of 84.0 The 1.03-acres is routed into a
pond at the north of the site and restricts outlet by a 12” reinforced concrete pipe (RCP)
at an invert of 827.68 with slope equal to 2.36% into the storm manhole northwest of the
site. The upstream invert of the manhole outfall at an invert of 826.41 will be the vertical
control for the drainage design of the project site. An evaluation of the pre-developed site
runoff volume and peak discharge rate was performed for the 2- and 10-year storm events
to gain an understanding of existing depressional storage system. The peak flows were
determined for the 24-hour storms using the SCS type II distribution. The minimum time
Culver’s – Carmel Weihe Engineers, Inc.
Stormwater Technical Report August 12, 2022
of concentration of 5-minutes were used due to the size and cover of the site. Please refer
to Section 2: Existing Drainage Calculations for details of the analysis.
The subject tract consists entirely of the soil type Urban Land – Miami Silt Loam
Complex (UkbB2), a C hydrologic soil. An abbreviated NRCS Soil Resource Report can
be found in the Appendix of this report.
Proposed Drainage:
The proposed Culver’s, on approximately 1.16 acres, located at 431 East Carmel Drive in
Carmel, Indiana will have an onsite stormwater management system to regulate the
stormwater that discharges the site. Per the City of Carmel Stormwater Technical
Standards Manual (SWTSM), Section 302.03, “Site- specific release rates for sites with
depressional storage” must be restricted such that the proposed 10-year peak runoff rate
matches that of the existing 2-year peak runoff rate and that the proposed 100-year peak
runoff rate matches that of the existing 10-year peak runoff rate.
Allowable Release Rates:
Q10post ≤ Q2pre = 2.90 cfs
Q100post ≤ Q2pre = 4.35 cfs
An outlet control structure with an orifice plate will be used to restrict flow from the site
to desired discharge rates, while an underground detention system will provide storage
caused by the flow restriction. The underground detention system was designed in
assistance by Contech Engineered Solutions using a combination of 40% porosity stone
and their ChamberMaxx chambers to provide a total of 5,457 cuft of storage, providing a
factor of safety of 1.10 in case of silt build up in the system. A 6” perforated subsurface
drain (SSD) will be laid along the perimeter of the system at an invert equal to 826.60 to
capture water that sinks into the stone base from the chambers. The chambers and SSD
will connect to an outlet control structure with 12” outfall RCP laid at 0.41% to the
existing outfall manhole. An orifice plate with an opening of 3.5” by 24” at an invert of
826.60 will be mounted to the manhole in order to restrict flow to allowable rates. The
top of the orifice plate shall be at an elevation of 830.25 to act as an overflow spillway to
allow higher order storms to bypass the restriction. The stormwater management design
and analysis utilized Autodesk’s Hydraflow Hydrographs extension of Autocad Civil 3d,
version 2021. See printouts of the model input and results under Section 3: Proposed
Drainage Calculations. The Hydraflow model analyzed the 2, 10 and 100-year return
interval storms to determine the peak flows for the 24-hour storms using the SCS type II
distribution. The minimum time of concentration of 5-minutes were used due to the size
and cover of the site. The peak storage volume for the 100-year event, was used for sizing
of the underground detention system. Summary of the design results are provided on the
next page.
Culver’s – Carmel Weihe Engineers, Inc.
Stormwater Technical Report August 12, 2022
Proposed Drainage Basin Peak Release Rates (cfs):
2-Year 10-Year 100-Year
Detention Discharge 1.70 2.62 3.72
Direct Discharge 0.28 0.50 1.03
Total Release 1.72 2.45 4.35
Underground Detention Peak Stage and Storage:
2-Year 10-Year 100-Year
Peak Stage (elev.) 827.96 828.70 830.00
Peak Storage (cuft) 1,950 3,275 4,909
*Storage capacity increased 10% from 4,980 to 5,482 cuft to account for sediment
Storm Sewers:
The storm sewer system is designed to convey stormwater runoff at a minimum velocity
of 2.5 feet/second through RCP while maintaining a hydraulic grade line elevation below
the top of castings during a 10-year storm event. For sizing of the storm sewer network,
the control basin was broken down further into three (3) contributing sub-basins, based
on proposed grading plans and structure locations.
The southwest subbasin (106) drains 0.27-acres with a runoff coefficient of 0.65, the
southeast subbasin (105) drains 0.26-acres with a runoff coefficient of 0.67, and the north
subbasin (104) drains 0.49-acres with a runoff coefficient of 0.74. Structure 106 connects
to Structure 105 by a 12” reinforced concrete pipe (RCP) at 0.32% and Structure 105
connects to Structure 104 by a 15” RCP at 0.32%. All structures are 30”x30” Type “E”
area inlets. The runoff is then routed to a diversion structure that directs main flow to a
water quality system, ending in the underground detention system. Figure 4 highlights
the site’s subbasins and storm sewer network through the site. Along with sizing the
storm sewer network for the 10-year storm, analysis was also performed for the 100-year
storm to check for ponding conditions. According to the city of Carmel’s (SWTSM), the
maximum ponding depth is 6”, but as both inlets are designed as sag inlets and the 100-
year storm remains below top of casting, ponding is not expected to occur. If inlets
become clogged, ponding will occur at a maximum of 6” before topping over towards the
next catch basin or discharging from the site. Figure 4.1 shows that emergency flood
routing will include structure 106 spilling into structure 105, structure 105 spilling into
the east adjoiner’s, Fazoli’s, west parking area, spiling into structure 104, which will spill
into the city’s right-of-way. Lidar data was collected from OpenTopography, an open-
source platform by the National Science Foundation, to provide contour elevations
Culver’s – Carmel Weihe Engineers, Inc.
Stormwater Technical Report August 12, 2022
through the Fazoli site. Please refer to Section 4: Storm Sewer Calculations for further
details of the pipe sizing calculations.
Water Quality:
Site runoff from the captured drainage area of the proposed Culver’s will be treated to
follow Chapter 700 of the City of Carmel’s (SWTSM). With the site being a
redevelopment of over 1-acre, pre-treatment best management practices (BMP’s) are
required before releasing runoff from the site. The Curve Number Method was used to
determine the runoff volume expected for the water quality unit, which when combined
with the unit peak discharge rate from the NRCS type II rainfall distribution led to a
treatment flowrate of 1.12cfs. Runoff will be directed through an Aqua-Swirl XCelerator-
3, which can serve a maximum flowrate of 1.13cfs. Along with the XCelerator, all catch
basins will be mounted by an Aqua-Swirl Aqua-Guardian inlet insert filter to act as the
first bmp in the treatment train. Refer to Section 5: Water Quality Calculations for
further details.
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PROJECT LOCATION
October 19, 2022FIGURE 1
WEIHE weihe.net
Indianapolis, Indiana 46280
10505 N. College Avenue
317 | 846 - 6611E N G I N E E R S
W
S
N
ECulver's
Carmel, IN
PROJECT LOCATION
SITE AERIAL
October 19, 2022FIGURE 1.1
WEIHE weihe.net
Indianapolis, Indiana 46280
10505 N. College Avenue
317 | 846 - 6611E N G I N E E R S
W
S
N
ECulver's
Carmel, IN
PROJECT LOCATION
SECTION 2:
EXISTING DRAINAGE
CALCULATIONS
CCCCCCCCCCCCC6" STORM -PREFERREDLOCATION4" FOODWASTE4" SANWASTEGAS SERVICECT CABSTORM DROP FROM ROOF -PREFERRED LOCATIONTHIS AREA IS FOR MENU BOARDS AND OCB ONLY.NO UNDERGROUND GREASE TRAPS OR ABOVEGROUND ELECTRICAL TRANSFORMERS; SEE SITEPLAN FROM CFS.VERIFY ALL UNDERGROUND WORK THIS AREA w/SIGN CONTRACTOR.FIRE PROTECTION2" WATER SERVICEFDCDIRECT CONNECTIONSFOR VENDORSPICKUP WINDOWFIGURE 2EXISTING DRAINAGEBASIN MAPOctober 19, 2022WEIHEweihe.netIndianapolis, Indiana 4628010505 N. College Avenue317 | 846 - 6611E N G I N E E R SCULVER'SCARMEL, INWSNECAPTURED DETENTIONAREA: 1.03 ACRESCN: 88.6DIRECT DISCHARGEAREA: 0.13 ACRESCN: 84.0EX. 12" RCP22FT @ 2.36%
Project:
Date:
Job No:
Prepared By:
Checked By:
BASIN: Total Site
Cover type Area (SF) Area (Ac.) CN C
Pavement 18218 0.42 98 0.85
Roof 4470 0.10 98 0.90
Grass 27778 0.64 80 0.35
TOTAL =1.16 88.1 0.58
BASIN:
Cover type Area (SF) Area (Ac.) CN C
Pavement 16921 0.39 98 0.85
Roof 4470 0.10 98 0.90
Grass 23266 0.53 80 0.25
TOTAL =1.03 88.6 0.54
BASIN:
Cover type Area (SF) Area (Ac.) CN C
Pavement 1297 0.03 98 0
Roof 0 0.00 98 0.90
Grass 4512 0.10 80 0.25
TOTAL =0.13 84.0 0.19
Existing Runoff
Calculations
Carmel, IN Culver's
April 29, 2022
W220058
DEG
SSR
Captured Detention
Direct Discharge
HYDROGRAPH NO.1:
CAPTURED DETENTION
AREA: 1.03
CN: 88.6
Watershed Model Schematic Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Project: Existing.gpw Wednesday, 02 / 23 / 2022
Hyd.Origin Description
Legend
1 SCS Runoff Captured Detention
2 SCS Runoff Direct Discharge
3 Reservoir Detention Outlet
4 Combine Total Site Discharge
HYDROGRAPH NO.2:
DIRECT DISCHARGE
AREA: 0.13
CN: 84.0
HYDROGRAPH NO.3:
DETENTION OUTLET
HYDROGRAPH NO.4:
TOTAL SITE DISCHARGE
Hydrograph Return Period Recap
Hyd. Hydrograph Inflow Peak Outflow (cfs) Hydrograph
No. type hyd(s) Description
(origin) 1-yr 2-yr 3-yr 5-yr 10-yr 25-yr 50-yr 100-yr
1 SCS Runoff ------ ------- 2.707 ------- ------- 4.768 ------- ------- ------- Captured Detention
2 SCS Runoff ------ ------- 0.274 ------- ------- 0.526 ------- ------- ------- Direct Discharge
3 Reservoir 1 ------- 2.624 ------- ------- 3.883 ------- ------- ------- Detention Outlet
4 Combine 2, 3 ------- 2.898 ------- ------- 4.346 ------- ------- ------- Total Site Discharge
Proj. file: Existing.gpw Wednesday, 02 / 23 / 2022
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Hydrograph Summary Report
Hyd. Hydrograph Peak Time Time to Hyd. Inflow Maximum Total Hydrograph
No. type flow interval Peak volume hyd(s) elevation strge used Description
(origin) (cfs) (min) (min) (cuft) (ft) (cuft)
1 SCS Runoff 2.707 2 716 5,515 ------ ------ ------ Captured Detention
2 SCS Runoff 0.274 2 718 553 ------ ------ ------ Direct Discharge
3 Reservoir 2.624 2 718 5,515 1 828.66 181 Detention Outlet
4 Combine 2.898 2 718 6,068 2, 3 ------ ------ Total Site Discharge
Existing.gpw Return Period: 2 Year Wednesday, 02 / 23 / 2022
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 1
Captured Detention
Hydrograph type = SCS Runoff Peak discharge = 2.707 cfs
Storm frequency = 2 yrs Time to peak = 11.93 hrs
Time interval = 2 min Hyd. volume = 5,515 cuft
Drainage area = 1.030 ac Curve number = 88.6
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 2.67 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 2 4 6 8 10 12 14 16 18 20 22 24
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
Q (cfs)
Time (hrs)
Captured Detention
Hyd. No. 1 -- 2 Year
Hyd No. 1
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 2
Direct Discharge
Hydrograph type = SCS Runoff Peak discharge = 0.274 cfs
Storm frequency = 2 yrs Time to peak = 11.97 hrs
Time interval = 2 min Hyd. volume = 553 cuft
Drainage area = 0.130 ac Curve number = 84
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 2.67 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 2 4 6 8 10 12 14 16 18 20 22 24 26
Q (cfs)
0.00 0.00
0.05 0.05
0.10 0.10
0.15 0.15
0.20 0.20
0.25 0.25
0.30 0.30
0.35 0.35
0.40 0.40
0.45 0.45
0.50 0.50
Q (cfs)
Time (hrs)
Direct Discharge
Hyd. No. 2 -- 2 Year
Hyd No. 2
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 3
Detention Outlet
Hydrograph type = Reservoir Peak discharge = 2.624 cfs
Storm frequency = 2 yrs Time to peak = 11.97 hrs
Time interval = 2 min Hyd. volume = 5,515 cuft
Inflow hyd. No. = 1 - Captured Detention Max. Elevation = 828.66 ft
Reservoir name = Dry Detention Pond Max. Storage = 181 cuft
Storage Indication method used.
0 2 4 6 8 10 12 14 16 18 20 22 24
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
Q (cfs)
Time (hrs)
Detention Outlet
Hyd. No. 3 -- 2 Year
Hyd No. 3 Hyd No. 1 Total storage used = 181 cuft
Pond Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Pond No. 1 - Dry Detention Pond
Pond Data
Contours -User-defined contour areas. Conic method used for volume calculation. Begining Elevation = 827.68 ft
Stage / Storage Table
Stage (ft) Elevation (ft) Contour area (sqft) Incr. Storage (cuft) Total storage (cuft)
0.00 827.68 00 0 0
0.32 828.00 06 1 1
1.32 829.00 746 274 274
2.32 830.00 1,612 1,151 1,426
3.32 831.00 2,366 1,977 3,402
Culvert / Orifice Structures Weir Structures
[A] [B] [C] [PrfRsr] [A] [B] [C] [D]
Rise (in)= 12.00 0.00 0.00 0.00
Span (in)= 12.00 0.00 0.00 0.00
No. Barrels = 1 0 0 0
Invert El. (ft)= 827.68 0.00 0.00 0.00
Length (ft)= 22.00 0.00 0.00 0.00
Slope (%)= 2.36 0.00 0.00 n/a
N-Value = .013 .013 .013 n/a
Orifice Coeff.= 0.60 0.60 0.60 0.60
Multi-Stage = n/a No No No
Crest Len (ft)= 0.00 0.00 0.00 0.00
Crest El. (ft)= 0.00 0.00 0.00 0.00
Weir Coeff.= 3.33 3.33 3.33 3.33
Weir Type = --- --- --- ---
Multi-Stage = No No No No
Exfil.(in/hr)= 0.000 (by Wet area)
TW Elev. (ft)= 0.00
Note: Culvert/Orifice outflows are analyzed under inlet (ic) and outlet (oc) control. Weir risers checked for orifice conditions (ic) and submergence (s).
Stage / Storage / Discharge Table
Stage Storage Elevation Clv A Clv B Clv C PrfRsr Wr A Wr B Wr C Wr D Exfil User Total
ft cuft ft cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs
0.00 0 827.68 0.00 --- --- --- --- --- --- --- --- --- 0.000
0.32 1 828.00 0.42 ic --- --- --- --- --- --- --- --- --- 0.418
1.32 274 829.00 3.42 ic --- --- --- --- --- --- --- --- --- 3.424
2.32 1,426 830.00 5.10 ic --- --- --- --- --- --- --- --- --- 5.101
3.32 3,402 831.00 6.35 ic --- --- --- --- --- --- --- --- --- 6.350
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 4
Total Site Discharge
Hydrograph type = Combine Peak discharge = 2.898 cfs
Storm frequency = 2 yrs Time to peak = 11.97 hrs
Time interval = 2 min Hyd. volume = 6,068 cuft
Inflow hyds. = 2, 3 Contrib. drain. area = 0.130 ac
0 2 4 6 8 10 12 14 16 18 20 22 24
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
Q (cfs)
Time (hrs)
Total Site Discharge
Hyd. No. 4 -- 2 Year
Hyd No. 4 Hyd No. 2 Hyd No. 3
Hydrograph Summary Report
Hyd. Hydrograph Peak Time Time to Hyd. Inflow Maximum Total Hydrograph
No. type flow interval Peak volume hyd(s) elevation strge used Description
(origin) (cfs) (min) (min) (cuft) (ft) (cuft)
1 SCS Runoff 4.768 2 716 9,959 ------ ------ ------ Captured Detention
2 SCS Runoff 0.526 2 716 1,072 ------ ------ ------ Direct Discharge
3 Reservoir 3.883 2 720 9,959 1 829.24 545 Detention Outlet
4 Combine 4.346 2 718 11,032 2, 3 ------ ------ Total Site Discharge
Existing.gpw Return Period: 10 Year Wednesday, 02 / 23 / 2022
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 1
Captured Detention
Hydrograph type = SCS Runoff Peak discharge = 4.768 cfs
Storm frequency = 10 yrs Time to peak = 11.93 hrs
Time interval = 2 min Hyd. volume = 9,959 cuft
Drainage area = 1.030 ac Curve number = 88.6
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 4.06 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0.0 2.0 4.0 6.0 8.0 10.0 12.0 14.0 16.0 18.0 20.0 22.0
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
5.00 5.00
Q (cfs)
Time (hrs)
Captured Detention
Hyd. No. 1 -- 10 Year
Hyd No. 1
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 2
Direct Discharge
Hydrograph type = SCS Runoff Peak discharge = 0.526 cfs
Storm frequency = 10 yrs Time to peak = 11.93 hrs
Time interval = 2 min Hyd. volume = 1,072 cuft
Drainage area = 0.130 ac Curve number = 84
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 4.06 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 2 4 6 8 10 12 14 16 18 20 22 24
Q (cfs)
0.00 0.00
0.10 0.10
0.20 0.20
0.30 0.30
0.40 0.40
0.50 0.50
0.60 0.60
0.70 0.70
0.80 0.80
0.90 0.90
1.00 1.00
Q (cfs)
Time (hrs)
Direct Discharge
Hyd. No. 2 -- 10 Year
Hyd No. 2
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 3
Detention Outlet
Hydrograph type = Reservoir Peak discharge = 3.883 cfs
Storm frequency = 10 yrs Time to peak = 12.00 hrs
Time interval = 2 min Hyd. volume = 9,959 cuft
Inflow hyd. No. = 1 - Captured Detention Max. Elevation = 829.24 ft
Reservoir name = Dry Detention Pond Max. Storage = 545 cuft
Storage Indication method used.
0 2 4 6 8 10 12 14 16 18 20 22 24 26
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
5.00 5.00
Q (cfs)
Time (hrs)
Detention Outlet
Hyd. No. 3 -- 10 Year
Hyd No. 3 Hyd No. 1 Total storage used = 545 cuft
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Wednesday, 02 / 23 / 2022
Hyd. No. 4
Total Site Discharge
Hydrograph type = Combine Peak discharge = 4.346 cfs
Storm frequency = 10 yrs Time to peak = 11.97 hrs
Time interval = 2 min Hyd. volume = 11,032 cuft
Inflow hyds. = 2, 3 Contrib. drain. area = 0.130 ac
0 2 4 6 8 10 12 14 16 18 20 22 24 26
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
5.00 5.00
Q (cfs)
Time (hrs)
Total Site Discharge
Hyd. No. 4 -- 10 Year
Hyd No. 4 Hyd No. 2 Hyd No. 3
SECTION 3:
PROPOSED DRAINAGE
CALCULATIONS
1-STY BRICK AND FRAME
COMMERCIAL BUILDING
C C C C C C
C C C C C
CC
6" STORM -PREFERREDLOCATION4" FOODWASTE4" SANWASTEGAS SERVICECT CABSTORM DROP FROM ROOF -PREFERRED LOCATIONTHIS AREA IS FOR MENU BOARDS AND OCB ONLY.NO UNDERGROUND GREASE TRAPS OR ABOVEGROUND ELECTRICAL TRANSFORMERS; SEE SITEPLAN FROM CFS.VERIFY ALL UNDERGROUND WORK THIS AREA w/SIGN CONTRACTOR.FIRE PROTECTION
2" WATER SERVICEFDC
DIRECT CONNECTIONSFOR VENDORSPICKUP WINDOWSTMSTMFFE = 834.00
STM STM
ST
ST
PATIO
ST
PROPOSED BMP
EASEMENT
PROPOSED BMPEASEMENTPROPOSED BMPEASEMENTFIGURE 3
PROPOSED DRAINAGE
BASIN MAP
October 19, 2022
WEIHE weihe.net
Indianapolis, Indiana 46280
10505 N. College Avenue
317 | 846 - 6611E N G I N E E R S
CULVER'S
CARMEL, IN W
S
N
E
CAPTURED DETENTION
AREA: 1.02 ACRES
CN: 92.5
DIRECT DISCHARGE
AREA: 0.14 ACRES
CN: 82.8
OUTLET
CONTROL
STRUCTURE
UNDERGROUND
DETENTION
AQUA-SWIRL
XCELERATOR XC-3
DIVERSION
STRUCTURE
STRUCTURE TO BE
MOUNTED WITH CATCH
BASIN INSERT BMP
STRUCTURE TO BE
MOUNTED WITH CATCH
BASIN INSERT BMP
STRUCTURE TO BE
MOUNTED WITH CATCH
BASIN INSERT BMP
Project:
Date:
Job No:
Prepared By:
Checked By:
BASIN:
Cover type Area (SF) Area (Ac.) CN C
Pavement 28917 0.66 98 0.85
Roof 5558 0.13 98 0.90
Grass 15991 0.37 77 0.25
TOTAL =1.16 91.3 0.67
BASIN:
Cover type Area (SF) Area (Ac.) CN C
Pavement 27230 0.63 98 0.85
Roof 5558 0.13 98 0.90
Grass 11602 0.27 77 0.25
TOTAL =1.02 92.5 0.70
BASIN:
Cover type Area (SF) Area (Ac.) CN C
Pavement 1687 0.04 98 0.85
Roof 0 0.00 98 0.90
Grass 4389 0.10 77 0.25
TOTAL =0.14 82.8 0.42
Captured Detention
Direct Discharge
Total Site
Proposed Runoff
Calculations
Carmel, IN Culver's
February 24, 2022
W220058
DEG
SSR
Watershed Model Schematic Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Project: Proposed.gpw Thursday, 02 / 24 / 2022
Hyd.Origin Description
Legend
1 SCS Runoff Captured Detention
2 SCS Runoff Direct Discharge
3 Reservoir Underground Detention
4 Combine Total Site Discharge
HYDROGRAPH NO. 1:
CAPTURED DETENTION
AREA: 1.02
CN: 92.5
HYDROGRAPH NO. 2:
DIRECT DISCHARGE
AREA: 0.14
CN: 82.8
HYDROGARPH NO. 3:
UNDERGROUND
DETENTION OUTLET
HYDROGARPH NO. 4:
TOTAL SITE DISCHARGE
Hydrograph Return Period Recap
Hyd. Hydrograph Inflow Peak Outflow (cfs) Hydrograph
No. type hyd(s)Description
(origin) 1-yr 2-yr 3-yr 5-yr 10-yr 25-yr 50-yr 100-yr
1 SCS Runoff ------ ------- 3.125 ------- ------- 4.841 ------- ------- 8.640 Captured Detention
2 SCS Runoff ------ ------- 0.276 ------- ------- 0.499 ------- ------- 1.027 Direct Discharge
3 Reservoir 1 ------- 1.522 ------- ------- 2.129 ------- ------- 3.724 Detention Discharge
4 Combine 2, 3 ------- 1.717 ------- ------- 2.446 ------- ------- 4.346 Total Site Discharge
Proj. file: Proposed Carmel Standards.gpw Friday, 04 / 29 / 2022
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Hydrograph Summary Report
Hyd. Hydrograph Peak Time Time to Hyd. Inflow Maximum Total Hydrograph
No. type flow interval Peak volume hyd(s) elevation strge used Description
(origin) (cfs) (min) (min) (cuft) (ft) (cuft)
1 SCS Runoff 3.125 2 716 6,546 ------ ------ ------ Captured Detention
2 SCS Runoff 0.276 2 718 555 ------------ ------ Direct Discharge
3 Reservoir 1.522 2 722 6,541 1 827.71 1,474 Detention Discharge
4 Combine 1.717 2 720 7,097 2, 3 ------ ------ Total Site Discharge
Proposed Carmel Standards.gpw Return Period: 2 Year Friday, 04 / 29 / 2022
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 1
Captured Detention
Hydrograph type = SCS Runoff Peak discharge = 3.125 cfs
Storm frequency = 2 yrs Time to peak = 716 min
Time interval = 2 min Hyd. volume = 6,546 cuft
Drainage area = 1.020 ac Curve number = 92.5
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 2.66 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 120 240 360 480 600 720 840 960 1080 1200 1320
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
Q (cfs)
Time (min)
Captured Detention
Hyd. No. 1 -- 2 Year
Hyd No. 1
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 2
Direct Discharge
Hydrograph type = SCS Runoff Peak discharge = 0.276 cfs
Storm frequency = 2 yrs Time to peak = 718 min
Time interval = 2 min Hyd. volume = 555 cuft
Drainage area = 0.140 ac Curve number = 82.8
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 2.66 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 1560
Q (cfs)
0.00 0.00
0.05 0.05
0.10 0.10
0.15 0.15
0.20 0.20
0.25 0.25
0.30 0.30
0.35 0.35
0.40 0.40
0.45 0.45
0.50 0.50
Q (cfs)
Time (min)
Direct Discharge
Hyd. No. 2 -- 2 Year
Hyd No. 2
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 3
Detention Discharge
Hydrograph type = Reservoir Peak discharge = 1.522 cfs
Storm frequency = 2 yrs Time to peak = 722 min
Time interval = 2 min Hyd. volume = 6,541 cuft
Inflow hyd. No. = 1 - Captured Detention Max. Elevation = 827.71 ft
Reservoir name = Underground Detention Max. Storage = 1,474 cuft
Storage Indication method used.
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 1560
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
Q (cfs)
Time (min)
Detention Discharge
Hyd. No. 3 -- 2 Year
Hyd No. 3 Hyd No. 1 Total storage used = 1,474 cuft
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 4
Total Site Discharge
Hydrograph type = Combine Peak discharge = 1.717 cfs
Storm frequency = 2 yrs Time to peak = 720 min
Time interval = 2 min Hyd. volume = 7,097 cuft
Inflow hyds. = 2, 3 Contrib. drain. area = 0.140 ac
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 1560
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
Q (cfs)
Time (min)
Total Site Discharge
Hyd. No. 4 -- 2 Year
Hyd No. 4 Hyd No. 2 Hyd No. 3
Hydrograph Summary Report
Hyd. Hydrograph Peak Time Time to Hyd. Inflow Maximum Total Hydrograph
No. type flow interval Peak volume hyd(s) elevation strge used Description
(origin) (cfs) (min) (min) (cuft) (ft) (cuft)
1 SCS Runoff 4.841 2 716 10,427 ------ ------ ------ Captured Detention
2 SCS Runoff 0.499 2 716 1,011 ------ ------ ------ Direct Discharge
3 Reservoir 2.129 2 722 10,422 1 828.28 2,530 Detention Discharge
4 Combine 2.446 2 720 11,434 2, 3 ------ ------ Total Site Discharge
Proposed Carmel Standards.gpw Return Period: 10 Year Friday, 04 / 29 / 2022
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 1
Captured Detention
Hydrograph type = SCS Runoff Peak discharge = 4.841 cfs
Storm frequency = 10 yrs Time to peak = 716 min
Time interval = 2 min Hyd. volume = 10,427 cuft
Drainage area = 1.020 ac Curve number = 92.5
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 3.83 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 120 240 360 480 600 720 840 960 1080 1200
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
5.00 5.00
Q (cfs)
Time (min)
Captured Detention
Hyd. No. 1 -- 10 Year
Hyd No. 1
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 2
Direct Discharge
Hydrograph type = SCS Runoff Peak discharge = 0.499 cfs
Storm frequency = 10 yrs Time to peak = 716 min
Time interval = 2 min Hyd. volume = 1,011 cuft
Drainage area = 0.140 ac Curve number = 82.8
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 3.83 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440
Q (cfs)
0.00 0.00
0.05 0.05
0.10 0.10
0.15 0.15
0.20 0.20
0.25 0.25
0.30 0.30
0.35 0.35
0.40 0.40
0.45 0.45
0.50 0.50
Q (cfs)
Time (min)
Direct Discharge
Hyd. No. 2 -- 10 Year
Hyd No. 2
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 3
Detention Discharge
Hydrograph type = Reservoir Peak discharge = 2.129 cfs
Storm frequency = 10 yrs Time to peak = 722 min
Time interval = 2 min Hyd. volume = 10,422 cuft
Inflow hyd. No. = 1 - Captured Detention Max. Elevation = 828.28 ft
Reservoir name = Underground Detention Max. Storage = 2,530 cuft
Storage Indication method used.
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 1560
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
5.00 5.00
Q (cfs)
Time (min)
Detention Discharge
Hyd. No. 3 -- 10 Year
Hyd No. 3 Hyd No. 1 Total storage used = 2,530 cuft
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 4
Total Site Discharge
Hydrograph type = Combine Peak discharge = 2.446 cfs
Storm frequency = 10 yrs Time to peak = 720 min
Time interval = 2 min Hyd. volume = 11,434 cuft
Inflow hyds. = 2, 3 Contrib. drain. area = 0.140 ac
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 1560
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
Q (cfs)
Time (min)
Total Site Discharge
Hyd. No. 4 -- 10 Year
Hyd No. 4 Hyd No. 2 Hyd No. 3
Hydrograph Summary Report
Hyd. Hydrograph Peak Time Time to Hyd. Inflow Maximum Total Hydrograph
No. type flow interval Peak volume hyd(s) elevation strge used Description
(origin) (cfs) (min) (min) (cuft) (ft) (cuft)
1 SCS Runoff 8.640 2 716 19,368 ------ ------ ------ Captured Detention
2 SCS Runoff 1.027 2 716 2,143 ------ ------ ------ Direct Discharge
3 Reservoir 3.724 2 722 19,363 1 830.00 4,909 Detention Discharge
4 Combine 4.346 2 720 21,506 2, 3 ------ ------ Total Site Discharge
Proposed Carmel Standards.gpw Return Period: 100 Year Friday, 04 / 29 / 2022
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 1
Captured Detention
Hydrograph type = SCS Runoff Peak discharge = 8.640 cfs
Storm frequency = 100 yrs Time to peak = 716 min
Time interval = 2 min Hyd. volume = 19,368 cuft
Drainage area = 1.020 ac Curve number = 92.5
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 6.46 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 120 240 360 480 600 720 840 960 1080 1200
Q (cfs)
0.00 0.00
2.00 2.00
4.00 4.00
6.00 6.00
8.00 8.00
10.00 10.00
Q (cfs)
Time (min)
Captured Detention
Hyd. No. 1 -- 100 Year
Hyd No. 1
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 2
Direct Discharge
Hydrograph type = SCS Runoff Peak discharge = 1.027 cfs
Storm frequency = 100 yrs Time to peak = 716 min
Time interval = 2 min Hyd. volume = 2,143 cuft
Drainage area = 0.140 ac Curve number = 82.8
Basin Slope = 0.0 % Hydraulic length = 0 ft
Tc method = User Time of conc. (Tc) = 5.00 min
Total precip. = 6.46 in Distribution = Type II
Storm duration = 24 hrs Shape factor = 484
0 120 240 360 480 600 720 840 960 1080 1200 1320
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
Q (cfs)
Time (min)
Direct Discharge
Hyd. No. 2 -- 100 Year
Hyd No. 2
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 3
Detention Discharge
Hydrograph type = Reservoir Peak discharge = 3.724 cfs
Storm frequency = 100 yrs Time to peak = 722 min
Time interval = 2 min Hyd. volume = 19,363 cuft
Inflow hyd. No. = 1 - Captured Detention Max. Elevation = 830.00 ft
Reservoir name = Underground Detention Max. Storage = 4,909 cuft
Storage Indication method used.
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 1560
Q (cfs)
0.00 0.00
2.00 2.00
4.00 4.00
6.00 6.00
8.00 8.00
10.00 10.00
Q (cfs)
Time (min)
Detention Discharge
Hyd. No. 3 -- 100 Year
Hyd No. 3 Hyd No. 1 Total storage used = 4,909 cuft
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 4
Total Site Discharge
Hydrograph type = Combine Peak discharge = 4.346 cfs
Storm frequency = 100 yrs Time to peak = 720 min
Time interval = 2 min Hyd. volume = 21,506 cuft
Inflow hyds. = 2, 3 Contrib. drain. area = 0.140 ac
0 120 240 360 480 600 720 840 960 1080 1200 1320 1440 1560
Q (cfs)
0.00 0.00
1.00 1.00
2.00 2.00
3.00 3.00
4.00 4.00
5.00 5.00
Q (cfs)
Time (min)
Total Site Discharge
Hyd. No. 4 -- 100 Year
Hyd No. 4 Hyd No. 2 Hyd No. 3
Pond Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Pond No. 1 - Underground Detention
Pond Data
UG Chambers -Invert elev. = 827.10 ft, Rise x Span = 2.50 x 4.28 ft, Barrel Len = 98.10 ft, No. Barrels = 4, Slope = 0.10%, Headers = Yes
Encasement -Invert elev. = 826.60 ft, Width = 4.75 ft, Height = 4.00 ft, Voids = 40.00%
Stage / Storage Table
Stage (ft) Elevation (ft) Contour area (sqft) Incr. Storage (cuft)Total storage (cuft)
0.00 826.60 n/a 0 0
0.41 827.01 n/a 295 295
0.82 827.42 n/a 634 929
1.23 827.83 n/a 779 1,708
1.64 828.24 n/a 758 2,466
2.05 828.65 n/a 722 3,188
2.46 829.06 n/a 665 3,853
2.87 829.47 n/a 573 4,426
3.28 829.88 n/a 386 4,812
3.69 830.29 n/a 335 5,147
4.10 830.70 n/a 335 5,482
Culvert / Orifice Structures Weir Structures
[A] [B] [C] [PrfRsr] [A] [B] [C] [D]
Rise (in)= 12.00 3.50 Inactive 0.00
Span (in)= 12.00 24.00 0.00 0.00
No. Barrels = 1 1 1 0
Invert El. (ft)= 826.60 826.60 0.00 0.00
Length (ft)= 25.50 0.00 0.00 0.00
Slope (%)= 0.63 0.00 0.00 n/a
N-Value = .013 .013 .013 n/a
Orifice Coeff.= 0.60 0.60 0.60 0.60
Multi-Stage = n/a Yes Yes No
Crest Len (ft)= 0.00 0.00 0.00 0.00
Crest El. (ft)= 0.00 0.00 0.00 0.00
Weir Coeff.= 3.33 3.33 3.33 3.33
Weir Type = --- --- --- ---
Multi-Stage = No NoNoNo
Exfil.(in/hr)= 0.000 (by Wet area)
TW Elev. (ft)= 0.00
Note: Culvert/Orifice outflows are analyzed under inlet (ic) and outlet (oc) control. Weir risers checked for orifice conditions (ic) and submergence (s).
Stage / Storage / Discharge Table
Stage Storage Elevation Clv A Clv B Clv C PrfRsr Wr A Wr B Wr C Wr D Exfil User Total
ft cuft ft cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs
0.00 0 826.60 0.00 0.00 --- --- --- --- --- --- --- --- 0.000
0.41 295 827.01 0.54 oc 0.54 ic --- --- --- --- --- --- --- --- 0.544
0.82 929 827.42 1.18 oc 1.18 ic --- --- --- --- --- --- --- --- 1.178
1.23 1,708 827.83 1.64 oc 1.64 ic --- --- --- --- --- --- --- --- 1.636
1.64 2,466 828.24 2.08 oc 2.08 ic --- --- --- --- --- --- --- --- 2.082
2.05 3,188 828.65 2.56 oc 2.56 ic --- --- --- --- --- --- --- --- 2.561
2.46 3,853 829.06 2.96 oc 2.96 ic --- --- --- --- --- --- --- --- 2.963
2.87 4,426 829.47 3.32 oc 3.32 ic --- --- --- --- --- --- --- --- 3.317
3.28 4,812 829.88 3.64 oc 3.64 ic --- --- --- --- --- --- --- --- 3.637
3.69 5,147 830.29 3.93 oc 3.93 ic --- --- --- --- --- --- --- --- 3.930
4.10 5,482 830.70 4.20 oc 4.20 ic --- --- --- --- --- --- --- --- 4.204
Hydrograph Report
Hydraflow Hydrographs Extension for Autodesk® Civil 3D® by Autodesk, Inc. v2021 Friday, 04 / 29 / 2022
Hyd. No. 3
Detention Discharge
Hydrograph type = Reservoir Peak discharge = 3.724 cfs
Storm frequency = 100 yrs Time to peak = 722 min
Time interval = 2 min Hyd. volume = 19,363 cuft
Inflow hyd. No. = 1 - Captured DetentionReservoir name = Underground Deten
Max. Elevation = 830.00 ft Max. Storage = 4,909 cuft
Storage Indication method used.
Hydrograph Discharge Table ( Printed values >= 1.00% of Qp. Print interval = 10)
Time Inflow Elevation Clv A Clv B Clv C PfRsr Wr A Wr B Wr C Wr D Exfil Outflow
(min) cfs ft cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs
320 0.045 826.70 0.043 0.041 ----- ----- ----- ----- ----- ----- ----- 0.041
340 0.051 826.70 0.049 0.047 ----- ----- ----- ----- ----- ----- ----- 0.047
360 0.057 826.71 0.055 0.053 ----- ----- ----- ----- ----- ----- ----- 0.053
380 0.063 826.72 0.061 0.059 ----- ----- ----- ----- ----- ----- ----- 0.059
400 0.068 826.72 0.067 0.064 ----- ----- ----- ----- ----- ----- ----- 0.064
420 0.074 826.73 0.073 0.071 ----- ----- ----- ----- ----- ----- ----- 0.071
440 0.080 826.73 0.079 0.077 ----- ----- ----- ----- ----- ----- ----- 0.077
460 0.086 826.74 0.084 0.083 ----- ----- ----- ----- ----- ----- ----- 0.083
480 0.092 826.74 0.090 0.089 ----- ----- ----- ----- ----- ----- ----- 0.089
500 0.107 826.75 0.100 0.099 ----- ----- ----- ----- ----- ----- ----- 0.099
520 0.125 826.77 0.117 0.116 ----- ----- ----- ----- ----- ----- ----- 0.116
540 0.144 826.78 0.136 0.136 ----- ----- ----- ----- ----- ----- ----- 0.136
560 0.151 826.79 0.149 0.148 ----- ----- ----- ----- ----- ----- ----- 0.148
580 0.163 826.80 0.157 0.156 ----- ----- ----- ----- ----- ----- ----- 0.156
600 0.194 826.81 0.184 0.183 ----- ----- ----- ----- ----- ----- ----- 0.183
620 0.237 826.84 0.222 0.221 ----- ----- ----- ----- ----- ----- ----- 0.221
640 0.293 826.86 0.274 0.273 ----- ----- ----- ----- ----- ----- ----- 0.273
660 0.371 826.90 0.345 0.345 ----- ----- ----- ----- ----- ----- ----- 0.345
680 0.536 826.97 0.484 0.484 ----- ----- ----- ----- ----- ----- ----- 0.484
700 2.091 827.21 0.884 0.876 ----- ----- ----- ----- ----- ----- ----- 0.876
Continues on next page...
Detention Discharge
Hydrograph Discharge Table
Time Inflow Elevation Clv A Clv B Clv C PfRsr Wr A Wr B Wr C Wr D Exfil Outflow
(min) cfs ft cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs
720 6.449 829.78 3.561 3.561 ----- ----- ----- ----- ----- ----- ----- 3.561
740 0.845 828.55 2.459 2.459 ----- ----- ----- ----- ----- ----- ----- 2.459
760 0.496 827.71 1.530 1.528 ----- ----- ----- ----- ----- ----- ----- 1.528
780 0.391 827.20 0.865 0.860 ----- ----- ----- ----- ----- ----- ----- 0.860
800 0.326 826.95 0.435 0.435 ----- ----- ----- ----- ----- ----- ----- 0.435
820 0.274 826.87 0.293 0.293 ----- ----- ----- ----- ----- ----- ----- 0.293
840 0.234 826.85 0.247 0.246 ----- ----- ----- ----- ----- ----- ----- 0.246
860 0.215 826.84 0.221 0.220 ----- ----- ----- ----- ----- ----- ----- 0.220
880 0.200 826.83 0.206 0.205 ----- ----- ----- ----- ----- ----- ----- 0.206
900 0.186 826.82 0.192 0.191 ----- ----- ----- ----- ----- ----- ----- 0.191
920 0.172 826.81 0.178 0.177 ----- ----- ----- ----- ----- ----- ----- 0.177
940 0.158 826.80 0.165 0.164 ----- ----- ----- ----- ----- ----- ----- 0.164
960 0.144 826.79 0.151 0.150 ----- ----- ----- ----- ----- ----- ----- 0.150
980 0.137 826.78 0.140 0.140 ----- ----- ----- ----- ----- ----- ----- 0.140
1000 0.132 826.78 0.135 0.134 ----- ----- ----- ----- ----- ----- ----- 0.134
1020 0.127 826.78 0.129 0.129 ----- ----- ----- ----- ----- ----- ----- 0.129
1040 0.122 826.77 0.124 0.124 ----- ----- ----- ----- ----- ----- ----- 0.124
1060 0.116 826.77 0.119 0.119 ----- ----- ----- ----- ----- ----- ----- 0.119
1080 0.111 826.76 0.114 0.114 ----- ----- ----- ----- ----- ----- ----- 0.114
1100 0.106 826.76 0.109 0.109 ----- ----- ----- ----- ----- ----- ----- 0.109
1120 0.101 826.76 0.104 0.104 ----- ----- ----- ----- ----- ----- ----- 0.104
1140 0.096 826.75 0.100 0.099 ----- ----- ----- ----- ----- ----- ----- 0.099
1160 0.091 826.75 0.095 0.093 ----- ----- ----- ----- ----- ----- ----- 0.094
1180 0.086 826.74 0.090 0.088 ----- ----- ----- ----- ----- ----- ----- 0.088
1200 0.081 826.74 0.085 0.083 ----- ----- ----- ----- ----- ----- ----- 0.083
1220 0.079 826.74 0.082 0.080 ----- ----- ----- ----- ----- ----- ----- 0.080
1240 0.078 826.73 0.080 0.079 ----- ----- ----- ----- ----- ----- ----- 0.079
1260 0.077 826.73 0.079 0.077 ----- ----- ----- ----- ----- ----- ----- 0.077
Continues on next page...
Detention Discharge
Hydrograph Discharge Table
Time Inflow Elevation Clv A Clv B Clv C PfRsr Wr A Wr B Wr C Wr D Exfil Outflow
(min) cfs ft cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs
1280 0.076 826.73 0.078 0.076 ----- ----- ----- ----- ----- ----- ----- 0.076
1300 0.075 826.73 0.077 0.075 ----- ----- ----- ----- ----- ----- ----- 0.075
1320 0.074 826.73 0.076 0.074 ----- ----- ----- ----- ----- ----- ----- 0.074
1340 0.073 826.73 0.076 0.073 ----- ----- ----- ----- ----- ----- ----- 0.073
1360 0.072 826.73 0.075 0.072 ----- ----- ----- ----- ----- ----- ----- 0.072
1380 0.071 826.73 0.074 0.071 ----- ----- ----- ----- ----- ----- ----- 0.071
1400 0.070 826.73 0.073 0.070 ----- ----- ----- ----- ----- ----- ----- 0.070
1420 0.069 826.73 0.072 0.069 ----- ----- ----- ----- ----- ----- ----- 0.069
1440 0.068 826.73 0.071 0.068 ----- ----- ----- ----- ----- ----- ----- 0.068
...End
WEIR PLATE INSTALLATION DETAIL
OUTLET CONTROL STRUCTURE "101"
April 28, 2022FIGURE 5
WEIHE weihe.net
Indianapolis, Indiana 46280
10505 N. College Avenue
317 | 846 - 6611E N G I N E E R S
BB
SECTION A-A SECTION B-B
A
A
PLAN VIEW
SECTION 4:
STORM SEWER
CALCULATIONS
1-STY BRICK AND FRAMECOMMERCIAL BUILDINGCCCCCCCCCCCCC6" STORM -PREFERREDLOCATION4" FOODWASTE4" SANWASTEGAS SERVICECT CABSTORM DROP FROM ROOF -PREFERRED LOCATIONTHIS AREA IS FOR MENU BOARDS AND OCB ONLY.NO UNDERGROUND GREASE TRAPS OR ABOVEGROUND ELECTRICAL TRANSFORMERS; SEE SITEPLAN FROM CFS.VERIFY ALL UNDERGROUND WORK THIS AREA w/SIGN CONTRACTOR.FIRE PROTECTION2" WATER SERVICEFDCDIRECT CONNECTIONSFOR VENDORSPICKUP WINDOWS
T
M
S
T
M GGG
G G G G G GFFE = 834.00STMSTMSTSTPATIOSTPROPOSED BMPEASEMENTPROPOSED BMP
EASEMENT
PROPOSED BMP
EASEMENT
FIGURE 4WEIHEweihe.netIndianapolis, Indiana 4628010505 N. College Avenue317 | 846 - 6611E N G I N E E R SPROPOSED PIPE SIZINGBASIN MAPOctober 19, 2022CULVER'SCARMEL, INSEWNSTR 105TOC = 831.85INV (N) = 828.40INV (W) = 828.50202' OF 15" RCP @ 0.32%39' OF 18" RCP @ 0.32%STR 104TOC = 831.00INV (NW) = 827.75INV (S) = 827.65STR 103TOC = 831.39INV (SE) = 827.57INV (NE) = 827.47INV (N) = 828.52STR WQTOC = 831.39INV IN = 827.37INV OUT = 827.37STR 102TOC = 831.65INV (S) = 827.27INV (SE) =827.27INV (W) =827.17STR 101TOC = 832.78INV = 826.60Catchment -104Area = 0.49 Ac.C = 0.74Catchment - 105Area = 0.26 Ac.C = 0.67Catchment - 106Area = 0.27 Ac.C = 0.65STR 106TOC = 832.00INV = 828.80PROPOSED DRAINAGE EASEMENT93' OF 12" RCP @ 0.32%
BASIN: 104
Area (SF) Area (Ac.) C
12497 0.29 0.85
4612 0.11 0.90
4096 0.09 0.25
TOTAL =21205 0.49 0.74
BASIN: 105
Area (SF) Area (Ac.) C
6981 0.16 0.85
946 0.02 0.90
3517 0.08 0.25
TOTAL =11444 0.26 0.67
BASIN: 106
Area (SF) Area (Ac.) C
7856 0.18 0.85
0 0.00 0.90
3885 0.09 0.25
TOTAL =11741 0.27 0.65
BASIN: Direct Discharge
Area (SF) Area (Ac.) C
1687 0.04 0.85
0 0.00 0.90
4389 0.10 0.25
TOTAL =6076 0.14 0.42
Proposed Subbasin
Runoff Calculations
Project:Carmel, IN Culver's
Date:April 28, 2022
Job No:W220058
Prepared By:DEG
Checked By:SSR
Pervious, Grass
Cover type
Impervious, Pavement
Cover type
Impervious, Pavement
Impervious, Roof
Impervious, Pavement
Impervious, Roof
Pervious, Grass
Impervious, Roof
Pervious, Grass
Cover type
Cover type
Impervious, Pavement
Impervious, Roof
Pervious, Grass
Project:
Date:
Job No:
Prepared By:
Checked By:
Area (ft2)Perimeter (ft)Weir Condition (d<0.3')
1.50 7.90 Orifice Condition (d>0.4')
2.00 8.70
Inlet 102 0.74 0.49
Inlet 103 0.67 0.26
Inlet 104 0.65 0.27
Q Weir Orifice
Controlling
Depth Maximum Depth
Str. # (cfs) (ft) (ft) (ft) 0.5 ft
104 2.64 0.48 0.29 0.29 OK Neenah R-3357-A
105 1.27 0.24 0.12 0.24 OK Neenah R-3405
106 1.28 0.25 0.12 0.25 OK Neenah R-3405
*Rainfall intensities obtained from NOAA
Atlas 14, Volume 2, Version 3 for
Indianapolis, IN
10-year
7.27
2.64
1.27
1.28
Proposed Inlet
Capacity Calculations
Carmel, IN Culver's
October 19, 2022
W220058
DEG
SSR
Catch Basin Neenah R-3357-A
50% Cogged Condition Inlet Evaluation
Runoff
Coefficient Area (Ac)
Rainfall Intensity
10-Year Storm
Peak Discharge Rates
Type of Casting
Catch Basin Neenah R-3405
© 2022 Microsoft Corporation © 2022 Maxar ©CNES (2022) Distribution Airbus DS © 2022 TomTom 1-STY BRICK AND FRAMECOMMERCIAL BUILDINGCCCC6" STORM -PREFERREDLOCATION4" FOODWASTE4" SANWASTEGAS SERVICECT CABSTORM DROP FROM ROOF -PREFERRED LOCATIONTHIS AREA IS FOR MENU BOARDS AND OCB ONLY.NO UNDERGROUND GREASE TRAPS OR ABOVEGROUND ELECTRICAL TRANSFORMERS; SEE SITEPLAN FROM CFS.VERIFY ALL UNDERGROUND WORK THIS AREA w/SIGN CONTRACTOR.FIRE PROTECTION2" WATER SERVICEFDCDIRECT CONNECTIONSFOR VENDORSPICKUP WINDOWGG G G GFFE = 834.00STMSTSTPATIOSTS
T
M
FIGURE 4.1WEIHEweihe.netIndianapolis, Indiana 4628010505 N. College Avenue317 | 846 - 6611E N G I N E E R SEMERGENCY FLOODROUTING PLANOctober 24, 2022CULVER'SCARMEL, INSEWNEX. INLETTC = 833.96STR. 106TC = 831.83STR. 105TC = 831.68STR. 104TC = 831.00STR. 103TC = 831.32STR. WQTC = 831.36STR. 102TC = 831.58STR. 101TC = 833.30EX. INLETTC = 833.31DEPTH = 0.47'ELEV = 832.30DEPTH = 0.60'ELEV = 832.30DEPTH = 0.22'ELEV = 831.22LIDAR TOPOGRAPHY SHOULD NOT BECHANGING THROUGHOUT THE BUILDINGFOUNDATION. ASSUMED FFE = 832.5EX. CITY INLETTC = 825.6EX. CITY INLETTC= 829.4EX. CITY INLETTC = 828.8EX. CITY INLETTC= 830.4
SECTION 5:
WATER QUALITY
CALCULATIONS
Project:
Date:
Job No:
Prepared By:
Checked By:
WQv = water quality volume ( acre-feet) Formulas:
P = 1-inch of rainfall
Rv = volumetric runoff coeffient
A = total site area
I = percent of impervious cover
Qv = Runoff Depth (in) WQv = A*Qv
CN = Water Quality Curve Number Fig. 9-1 Qwq = A*Qv*qu
qu = Unit Peak Discharge (cfs/mi^2/in) from TR-55 Exhibit 4-II
Total Area SF Imp. Area SF "I" Rv CN S Qv (in)WQv (ac-ft)Ia qu (csm/in)Qwq (cfs)
44390 32892 74% 0.72 97 0.31 0.71 0.060 0.062 1000 1.12
From Chart From Chart From Chart
Stormwater Quality Calculations
Carmel, IN Culver's
October 24, 2022
W220058
DEG
SSR
From Site Data
I = Total / Impervious Areas
Rv = 0.05 + 0.009 (I)
S = (1000/CN) - 10
Qv = (P - 0.2S)^2/(P + 0.8S)
Curve Number Method
City of Indianapolis Stormwater Quality Unit (SQU)
Selection Guide
Pg. 2 02/11/2020
Version 17.0
Manufactured
SQU SQU System Model
Max
Treatment
Flow
(cfs)
Max 10-yr
On-Line
Flow Rate
(cfs)
Cleanout
Depth
(Inches)
4-ft 1.12 2.95 9
6-ft 2.52 6.63 12
8-ft 4.49 11.81 15
10-ft 7.00 18.40 18
Hydro
International
Downstream
Defender1
12 ft 10.08 26.51 21
3-ft 0.85 1.84 9
4-ft 1.5 3.24 9
5-ft 2.35 5.08 9
6-ft 3.38 7.30 9
7-ft 4.60 9.94 9
Hydro
International
First Defense
High Capacity1
8-ft 6.00 12.96 9
HS-3 0.50 1.00 6
HS-4 0.88 1.76 6
HS-5 1.37 2.74 6
HS-6 1.98 3.96 6
HS-7 2.69 5.38 6
HS-8 3.52 7.04 6
HS-9 4.45 8.9 6
HS-10 5.49 10.98 6
HS-11 6.65 13.3 6
HydroStorm by
Hydroworks,
LLC1
HS-12 7.91 15.82 6
XC-2 0.57 1.16 6
XC-3 1.13 2.30 6
XC-4 1.86 3.79 6
XC-5 2.78 5.66 6
XC-6 3.88 7.90 6
XC-7 5.17 10.52 6
XC-8 6.64 13.51 6
XC-9 8.29 16.87 6
XC-10 10.13 20.62 6
XC-11 12.15 24.73 6
XC-12 14.35 29.20 6
AquaShield
Aqua-Swirl
Xcelerator1
XC-13 15.53 31.60 6
CS-4 1.80 4.03 9
CS-5 2.81 6.29 9
CS-6 4.05 9.07 9
CS-8 7.20 16.1 9
CS-10 11.3 25.3 9
Contech
Cascade
Separator
CS-12 16.2 36.3 9
OFF-LINE WATER QUALITY &
DIVERSION STRUCTURE DETAIL
April 28, 2022FIGURE 6
WEIHE weihe.net
Indianapolis, Indiana 46280
10505 N. College Avenue
317 | 846 - 6611E N G I N E E R S
OUTLET INVERT FROM STR 103 TO
STR 102 HAS BEEN RAISED FROM
ANALYSIS COMPUTATIONS TO ACT
AS A WEIR, ENSURING PRIMARY
FLOW IS DIRECTED TO AQUA-SWIRL
~39 L.F
18" RCP
~10 L.F 12" HDPE
STR 103
48" DIA MANHOLE
DIVERSION STR.
TOC = 831.39
INV = 828.52
INV = 827.47
INV = 827.37
INV = 827.27
INV = 827.27
INV = 827.17
INV = 827.57
INV = 827.37
~10 L.F 12" HDPE
~15 L.F
12" HDPE
STR 102
48" DIA MANHOLE
TOC = 831.65
AQUA-SWIRL
XCELERATOR XC-3
TOC = 831.39
Plan View
SCALE 1:40
Elevation View
SCALE 1:40
Projected View
SCALE 1:70
2733 Kanasita Drive, Suite 111, Chattanooga, TN 37343
Phone (888) 344-9044 Fax (423) 826-2112
www.aquashieldinc.com
Structure #:
Drawn By:
Scale:
Date:
OFlores
6/26/2019
Rvwed Rvw. Date
U.S. Patent No. 6524473 and other Patent Pending
Aqua-Swirl XCelerator
Aqua-Swirl Stormwater Treatment System
Standard Detail
As Shown
el. Varies
Inlet/Outlet Invert
el. Varies
el. Varies
Grade (Rim) el. Varies
XC-3 CCW STD
XC-3 STD
Aqua-Swirl Polymer Coated Steel (PCS)
Stormwater Treatment System
12 in
[305 mm]
Manhole Frame & Cover Detail
For Non-Traffic Areas Only
NTS
4 in
[1219 mm] Min.
Gravel Backfill
Concrete
Wrap Compressible Expansion
Joint Material to a minimum
1/2-inch [13 mm] thickness around
top of riser to allow transfer of
inadvertent loading from
manhole cover to concrete slab.
Riser
Soil
Cover
Frame
1/2 in
[13 mm]
1/2 in
[13 mm]
Place small amount of
concrete [3,000 psi [20
MPa] (min)] to support
and level manhole frame.
DO NOT allow manhole
frame to rest upon riser.
Backfill (90%
Proctor Density)
8 in
[203 mm]
4 1/2 in
[114 mm]
Unless other traffic barriers are present,
bollards shall be placed around access riser(s)
in non-traffic areas to prevent inadvertent
loading by maintenance vehicles.
Manhole Frame & Cover Detail
For Traffic Loading Areas
NTS
Cover
Frame
48 in
[1219 mm] Min.
Backfill (90%
Proctor Density)
3,000 psi [20 MPa]
(min) Concrete
#4 [13 mm] Rebar
@ 6 in [152 mm]
Each Way
30 in [762 mm]
Riser
1/2 in
[13 mm]
4 1/2 in
[114 mm]
14 in
[356 mm]
1/2 in [13 mm] Thick
Expansion Joint
Material
If traffic loading (HS-25) is required or anticipated, a 4-foot [1.22 m]
diameter, 14-inch [356 mm] thick reinforced concrete pad must be
placed over the Stormwater Treatment System Riser to support and
level the manhole frame, as shown. The top of riser pipe must be
wrapped with compressible expansion joint material to a minimum
1/2-inch [13 mm] thickness to allow transfer of wheel loads from
manhole cover to concrete slab. Manhole cover shall bear on concrete
slab and not on riser pipe. The concrete slab shall have a minimum
strength of 3,000 psi [20 MPa] and be reinforced with #4 [13 mm]
reinforcing steel as shown. Minimum cover over reinforcing steel shall
be 1-inch [25 mm]. Top of manhole cover and concrete slab shall be
level with finish grade.
Please see accompanied Aqua-Swirl specification notes. See Site
Plan for actual System orientation. Approximate dry (pick) weight:
1500 lbs [700 kg].
Backfill shall extend at least 18
inches [457 mm] outward from
Swirl Concentrator and for the
full height of the Swirl
Concentrator (including riser)
extending laterally to
undisturbed soils. (See MH
Detail Below)
Backfill
Bedding
Undisturbed soil
18 in
[457 mm]
6 in
[152 mm]
1
1
As an alternative, 42 in [1067 mm] diameter, HS-20/25
rated precast concrete rings may be substituted. 14 in
[356 mm] thickness must be maintained.
XC-3 inlet/outlet pipe size ranges up to 21 in [533 mm].
XC-3 chamber height may vary up to 80 in [2032 mm],
depending on inlet/outlet pipe size.
Orientation may vary from a minimum of 90 to a
maximum of 180. Clockwise or counterclockwise
orientation as needed.
2
3
3
2
54 in
[1372 mm]
54 in
[1372 mm]
P21 in
[P533 mm]
P21 in
[P533 mm]
2
Octagonal Base Plate
P42 in
[P1070 mm]
47 in
[1194 mm]
80 in
[2032 mm]
Varies Varies
5
[127 mm]
MH Frame
P30 in
[P762 mm]
Band Coupler
by Manufacturer.
(as needed)
Riser
Manhole Frame and
Cover by Manufacturer.
(See Details)
Rim elevations to
match finish grade.
Pipe coupling
by Contractor.
12 in [305 mm]
long Stub-out
by Manufacturer.
4
4
Pipe coupling
by Contractor.
12 in [305 mm]
long Stub-out
by Manufacturer.
180P42 in
[P1067 mm]
Optional inlet
orientations available
(See note 4)
Elevation View
SCALE 1:12
Plan View
SCALE 1:12
Projected View
SCALE 1:40
Mounting Rails
SCALE 1:12
QTY - 4
DETAIL A
SCALE 1:6
"T" Handle Center Piece Detail
SCALE 1:12
A
2733 Kanasita Drive, Suite 111, Chattanooga, TN 37343
Phone (888) 344-9044 Fax (423) 826-2112
www.aquashieldinc.com
Structure #:
Drawn By:
Scale:
Date:
OFlores
5/5/2020
Rvwed Rvw. Date
U.S. Patent Pending
Aqua-Guardian
Standard Detail
As Shown
Rev Date Description of RevisionAqua-Guardian Catch Basin Insert
GENERAL NOTES:
1. Insert shall be constructed from High-Density Polyethlene (HDPE)
PE 3408 ASTM F714 and stainless/powder coated steel.
2. HDPE support flange can be field cut by contractor to fit.
3. Prior to fabrication, purchaser is responsible for indicating all
obstructions in catch basin which might inhibit proper installation.
4. Optimum installation requires that the bottom of the insert be
above or level with the crown of discharge pipe elevation (1/2
discharge pipe minimum).
SIGNED APPROVED DRAWING REQUIRED BEFORE
START OF MANUFACTURING DATE:________
( ) APPROVED _____________________________
( ) APPROVED AS NOTED ____________________
( ) REVISE & RESUBMIT _____________________
AG-18 STD
AG-18
24"
24"
Contractor to Drill 3/8"
holes in HDPE Support
Flange to match Mounting Rails
Stainless Steel Mounting Ralls
to be installed by contractor
using stainless steel bolts, fender
washers/flat bar and lock nuts
(provided by manufacturer).
Filter Housing
Locking
Centerpiece
Filter Screen
Outlet Flow Filtered
Standpipe
Perforated
Base PlateFilter Media
Sediment Collection
Chamber
HDPE Support Flange
can be field cut by
contractor to fit.
Internal High Flow
Bypass
"T" Handle
21 1/2"
1"
HDPE Support Flange
(can be field cut
by contractor to fit)
24 1/2"
24"
2"
1"14"2"
2"5 3/4"7/8"1"
HDPE Suppot
Flange
Fender Washer
or Flat Bar
Lock Nut
Washer
5/16" BoltMounting Rail
P13 1/4"
Performance Evaluation
Using a Perlite Filter1
Aqua-Tech Report 7.3
AquaShield™, Inc. ● 2733 Kanasita Dr., Suite B ● Chattanooga, TN 37343
Phone: 423.870.8888 ● Fax: 423.826.2112 ● Toll-Free: 888.344.9044 ● www.aquashieldinc.com
Background Information
AquaShieldTM utilizes various filter media for the
treatment of stormwater and industrial runoff in the
Aqua-FilterTM Stormwater Filtration System, the Go-
FilterTM Mobile Treatment System, and the Aqua-
GuardianTM Catch Basin Insert. The media is
packaged in flexible cartridges that are fixed within
the different patented technology devices. While
each of these systems are custom-engineered
facilities, the Aqua-FilterTM and Go-FilterTM systems
utilize a two stage treatment train configuration.
Treatment begins with the removal of gross
pollutants and free-floating oil by the swirl
concentrator (Aqua-SwirlTM), followed by the
removal of fine sediments and other waterborne
pollutants by the filtration chamber. The Aqua-
GuardianTM does not rely on a treatment train
approach.
Perlite is the most common filter media used in the
AquaShieldTM stormwater treatment systems. Perlite
(CAS: 93763-70-3) is an amorphous, hydrated
glassy volcanic rock of rhyolitic composition,
consisting primarily of fused sodium potassium
aluminum silicate. Perlite has long been recognized
as an effective filter medium for the removal of
sediment and hydrocarbons contained in stormwater
runoff.
Purpose of Performance Evaluation
In order to evaluate the performance level of a
perlite filter medium, a laboratory simulation was
performed using known concentrations of common
contaminants associated with stormwater runoff.
Laboratory Methods
Independent laboratory testing was performed on
behalf of AquaShieldTM by Analytical Industrial
Research Laboratories, Inc. (AIRL) of Cleveland,
Tennessee.2 AIRL is accredited with the National
Environmental Laboratory Accreditation Program
(NELAP).
A 50 gallon stock solution of laboratory reagent
water containing known concentrations of total
suspended solids (TSS) aluminum, copper, zinc and
phosphorus was gravity fed from a 50-gallon sterile
polypropylene holding tank. The container was
gently stirred with an electric motor turning a paddle
at approximately 25°C (77°F). The container was
fitted at the base with a manually operated PVC flow
discharge nozzle. An open ended, tube shaped, PVC
filtration cartridge was held in place below the
discharge nozzle by the use of standard laboratory
clamp devices. A three inch (7.62 cm) head space
was maintained between the discharge nozzle and
the top of the filtration cartridge. The filtration
cartridge dimensions were six inches (15.24 cm) in
diameter and eight inches (20.32 cm) in length, and
occupied a volume of 226 cubic inches (3,705 cubic
cm). The cartridge contained 370 grams of
consolidated (not packed) perlite. Both ends of the
cartridge were covered with a thin flexible nylon
screen having one millimeter (0.0394 inch) square
openings to retain the perlite filter media.
Target influent concentrations were based on the
maximum concentration from two years of sampling
a commercial parking lot (Table 1).
Table 1: Target Influent Concentrations
Contaminant Maximum Concentration
TSS 44 mg/L
Aluminum 786 g/L
Copper 21.9 g/L
Zinc 118 g/L
Phosphorus 50 mg/L
All test constituents were insoluble forms. The
simulation used sediment (TSS) particle sizes of 19,
45 and 75 microns, ranging from silt to very fine-
grained sand. Particle sizes for the aluminum,
phosphorus and zinc were <10 microns, while the
copper particle size was <5 microns.
Water passed through the filtration cartridge at an
assigned flow, or loading rate of approximately 17.8
gpm/ft2 and at five gallon increments. One gallon
effluent (filtered) water samples were collected in
new, sterile polypropylene containers at the
terminus of the filtration cartridge at pre-determined
discharge volume intervals between the 4th and 5th,
24th and 25th gallon, and 49th and 50th gallon. Each
effluent water sample was analyzed for the
contaminant constituents and within their
Performance Evaluation
Using a Perlite Filter1
Aqua-Tech Report 7.3
AquaShield™, Inc. ● 2733 Kanasita Dr., Suite B ● Chattanooga, TN 37343
Phone: 423.870.8888 ● Fax: 423.826.2112 ● Toll-Free: 888.344.9044 ● www.aquashieldinc.com
established holding times. Prior to testing, the
filtration cartridge was rinsed with five gallons of
reagent water to establish background levels for
each constituent. The sampling for the “blanks”
occurred between the 4th and 5th gallon.
Laboratory analytical methods for influent and
effluent water samples followed EPA Method 160.2
for TSS and EPA Method 200.7 for the other
contaminants.
Simulated Test Parameters
The use of simulated test parameters allows for the
laboratory test parameters to be extrapolated in
order to evaluate removal efficiency for a larger
scale filtration cartridge. By using the laboratory test
parameters of test gallons (50 gallons), test
cartridge volume (226 in3) and loading rate (17.8
gpm/ft2), the extrapolated flow rate over a 24 hour
period using a larger simulated filtration cartridge
can be calculated.
Based on the laboratory test parameters cited above
and a simulated filtration cartridge measuring 2 feet
x 2 feet x 1 foot thick (4 ft3, or 6,912 in3), the
laboratory test simulated approximately 102,400
gallons of contaminated water continuously passing
through a 4 ft3 filtration cartridge over a 24 hour
period.
Analytical Results
Table 2 summarizes the average influent and
effluent concentrations of the contaminants, and the
calculated removal efficiencies that were achieved
during the performance test. Removal efficiency (RE,
%) is calculated as follows:
RE = 100 x Influent Concentration – Effluent Concentration
Influent Concentration
A removal efficiency of 100% is not calculated for a
recorded concentration that is below the method
detection limit (MDL). While it is possible that a very
small fraction of the contaminant could be contained
in the effluent water below the MDL, the use of a
reported effluent value of zero is not realistic. If the
concentration is reported as less than the MDL, then
one-half the MDL value is the reported concentration
Table 2: Perlite Filter Performance Summary
Contaminant* Average
Influent
Average
Effluent
Removal
Efficiency
(%)
TSS 50 2** 96.0
Aluminum 800 33 95.9
Copper 25 2.5** 90.0
Zinc 120 2.5** 97.9
Phosphorus 50 2 96.0
* TSS, P in mg/L; Al, Cu and Zn in g/L
** Listed value = ½ MDL
It should be kept in mind that the average effluent
concentrations for TSS, copper and zinc were
recorded below their respective MDLs.
The following graph illustrates the high removal
efficiencies achieved by the perlite filter medium
during the performance evaluation:
Perlite Filter Media Performance
96.0 95.9
90.0
97.9
96.0
80.0
85.0
90.0
95.0
100.0
TSS Aluminum Copper Zinc Phosphorus
Constituent ContaminantsRemoval Efficiency (%)Conclusion
Laboratory performance testing using approximately
100,000 gallons of simulated stormwater passing
through a 4 ft3 filtration cartridge in a 24 hour
period demonstrates that the perlite filter medium
provides outstanding water quality treatment against
the tested contaminants. The TSS removal efficiency
is calculated to be 96%, while excellent treatment
was also achieved against aluminum, copper, zinc
and phosphorus with removal efficiencies ranging
from 90 to 97.9%.
1 Jan. 2003, Updated Nov. 2007
2 AIRL, 1550 37th Street, NE, Cleveland, TN 37312,
(423) 476-7766.
SECTION 6:
APPENDIX
National Flood Hazard Layer FIRMette
0 500 1,000 1,500 2,000250
Feet
Ü
SEE FIS REPORT FOR DETAILED LEGEND AND INDEX MAP FOR FIRM PANEL LAYOUT
SPECIAL FLOOD
HAZARD AREAS
Without Base Flood Elevation (BFE)
Zone A, V, A99
With BFE or DepthZone AE, AO, AH, VE, AR
Regulatory Floodway
0.2% Annual Chance Flood Hazard, Areas
of 1% annual chance flood with average
depth less than one foot or with drainage
areas of less than one square mileZone X
Future Conditions 1% Annual
Chance Flood HazardZone X
Area with Reduced Flood Risk due to
Levee. See Notes.Zone X
Area with Flood Risk due to LeveeZone D
NO SCREEN Area of Minimal Flood Hazard Zone X
Area of Undetermined Flood HazardZone D
Channel, Culvert, or Storm Sewer
Levee, Dike, or Floodwall
Cross Sections with 1% Annual Chance
17.5 Water Surface Elevation
Coastal Transect
Coastal Transect Baseline
Profile Baseline
Hydrographic Feature
Base Flood Elevation Line (BFE)
Effective LOMRs
Limit of Study
Jurisdiction Boundary
Digital Data Available
No Digital Data Available
Unmapped
This map complies with FEMA's standards for the use of
digital flood maps if it is not void as described below.
The basemap shown complies with FEMA's basemap
accuracy standards
The flood hazard information is derived directly from the
authoritative NFHL web services provided by FEMA. This map
was exported on 2/1/2022 at 4:18 PM and does not
reflect changes or amendments subsequent to this date and
time. The NFHL and effective information may change or
become superseded by new data over time.
This map image is void if the one or more of the following map
elements do not appear: basemap imagery, flood zone labels,
legend, scale bar, map creation date, community identifiers,
FIRM panel number, and FIRM effective date. Map images for
unmapped and unmodernized areas cannot be used for
regulatory purposes.
Legend
OTHER AREAS OF
FLOOD HAZARD
OTHER AREAS
GENERAL
STRUCTURES
OTHER
FEATURES
MAP PANELS
8
B 20.2
The pin displayed on the map is an approximate
point selected by the user and does not represent
an authoritative property location.
1:6,000
86°7'27"W 39°57'55"N
86°6'50"W 39°57'27"N
Basemap: USGS National Map: Orthoimagery: Data refreshed October, 2020
United States
Department of
Agriculture
A product of the National
Cooperative Soil Survey,
a joint effort of the United
States Department of
Agriculture and other
Federal agencies, State
agencies including the
Agricultural Experiment
Stations, and local
participants
Custom Soil Resource
Report for
Hamilton
County, IndianaNatural
Resources
Conservation
Service
February 1, 2022
6
Custom Soil Resource Report
Soil Map
442378044237904423800442381044238204423830442384044238504423860442387044238804423890442390044239104423790442380044238104423820442383044238404423850442386044238704423880442389044239004423910575190 575200 575210 575220 575230 575240 575250 575260 575270 575280 575290
575190 575200 575210 575220 575230 575240 575250 575260 575270 575280 575290
39° 57' 43'' N 86° 7' 10'' W39° 57' 43'' N86° 7' 6'' W39° 57' 38'' N
86° 7' 10'' W39° 57' 38'' N
86° 7' 6'' WN
Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 16N WGS84
0 30 60 120 180
Feet
0 5 10 20 30
Meters
Map Scale: 1:674 if printed on A portrait (8.5" x 11") sheet.
Soil Map may not be valid at this scale.
MAP LEGEND MAP INFORMATION
Area of Interest (AOI)
Area of Interest (AOI)
Soils
Soil Map Unit Polygons
Soil Map Unit Lines
Soil Map Unit Points
Special Point Features
Blowout
Borrow Pit
Clay Spot
Closed Depression
Gravel Pit
Gravelly Spot
Landfill
Lava Flow
Marsh or swamp
Mine or Quarry
Miscellaneous Water
Perennial Water
Rock Outcrop
Saline Spot
Sandy Spot
Severely Eroded Spot
Sinkhole
Slide or Slip
Sodic Spot
Spoil Area
Stony Spot
Very Stony Spot
Wet Spot
Other
Special Line Features
Water Features
Streams and Canals
Transportation
Rails
Interstate Highways
US Routes
Major Roads
Local Roads
Background
Aerial Photography
The soil surveys that comprise your AOI were mapped at
1:15,800.
Warning: Soil Map may not be valid at this scale.
Enlargement of maps beyond the scale of mapping can cause
misunderstanding of the detail of mapping and accuracy of soil
line placement. The maps do not show the small areas of
contrasting soils that could have been shown at a more detailed
scale.
Please rely on the bar scale on each map sheet for map
measurements.
Source of Map: Natural Resources Conservation Service
Web Soil Survey URL:
Coordinate System: Web Mercator (EPSG:3857)
Maps from the Web Soil Survey are based on the Web Mercator
projection, which preserves direction and shape but distorts
distance and area. A projection that preserves area, such as the
Albers equal-area conic projection, should be used if more
accurate calculations of distance or area are required.
This product is generated from the USDA-NRCS certified data as
of the version date(s) listed below.
Soil Survey Area: Hamilton County, Indiana
Survey Area Data: Version 22, Sep 9, 2021
Soil map units are labeled (as space allows) for map scales
1:50,000 or larger.
Date(s) aerial images were photographed: Aug 1, 2018—Sep
30, 2018
The orthophoto or other base map on which the soil lines were
compiled and digitized probably differs from the background
imagery displayed on these maps. As a result, some minor
shifting of map unit boundaries may be evident.
Custom Soil Resource Report
7
Map Unit Legend
Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI
UkbB2 Urban land-Miami silt loam
complex, 2 to 6 percent
slopes, eroded
1.3 100.0%
Totals for Area of Interest 1.3 100.0%
Map Unit Descriptions
The map units delineated on the detailed soil maps in a soil survey represent the
soils or miscellaneous areas in the survey area. The map unit descriptions, along
with the maps, can be used to determine the composition and properties of a unit.
A map unit delineation on a soil map represents an area dominated by one or more
major kinds of soil or miscellaneous areas. A map unit is identified and named
according to the taxonomic classification of the dominant soils. Within a taxonomic
class there are precisely defined limits for the properties of the soils. On the
landscape, however, the soils are natural phenomena, and they have the
characteristic variability of all natural phenomena. Thus, the range of some
observed properties may extend beyond the limits defined for a taxonomic class.
Areas of soils of a single taxonomic class rarely, if ever, can be mapped without
including areas of other taxonomic classes. Consequently, every map unit is made
up of the soils or miscellaneous areas for which it is named and some minor
components that belong to taxonomic classes other than those of the major soils.
Most minor soils have properties similar to those of the dominant soil or soils in the
map unit, and thus they do not affect use and management. These are called
noncontrasting, or similar, components. They may or may not be mentioned in a
particular map unit description. Other minor components, however, have properties
and behavioral characteristics divergent enough to affect use or to require different
management. These are called contrasting, or dissimilar, components. They
generally are in small areas and could not be mapped separately because of the
scale used. Some small areas of strongly contrasting soils or miscellaneous areas
are identified by a special symbol on the maps. If included in the database for a
given area, the contrasting minor components are identified in the map unit
descriptions along with some characteristics of each. A few areas of minor
components may not have been observed, and consequently they are not
mentioned in the descriptions, especially where the pattern was so complex that it
was impractical to make enough observations to identify all the soils and
miscellaneous areas on the landscape.
The presence of minor components in a map unit in no way diminishes the
usefulness or accuracy of the data. The objective of mapping is not to delineate
pure taxonomic classes but rather to separate the landscape into landforms or
landform segments that have similar use and management requirements. The
delineation of such segments on the map provides sufficient information for the
development of resource plans. If intensive use of small areas is planned, however,
Custom Soil Resource Report
8
onsite investigation is needed to define and locate the soils and miscellaneous
areas.
An identifying symbol precedes the map unit name in the map unit descriptions.
Each description includes general facts about the unit and gives important soil
properties and qualities.
Soils that have profiles that are almost alike make up a soil series. Except for
differences in texture of the surface layer, all the soils of a series have major
horizons that are similar in composition, thickness, and arrangement.
Soils of one series can differ in texture of the surface layer, slope, stoniness,
salinity, degree of erosion, and other characteristics that affect their use. On the
basis of such differences, a soil series is divided into soil phases. Most of the areas
shown on the detailed soil maps are phases of soil series. The name of a soil phase
commonly indicates a feature that affects use or management. For example, Alpha
silt loam, 0 to 2 percent slopes, is a phase of the Alpha series.
Some map units are made up of two or more major soils or miscellaneous areas.
These map units are complexes, associations, or undifferentiated groups.
A complex consists of two or more soils or miscellaneous areas in such an intricate
pattern or in such small areas that they cannot be shown separately on the maps.
The pattern and proportion of the soils or miscellaneous areas are somewhat similar
in all areas. Alpha-Beta complex, 0 to 6 percent slopes, is an example.
An association is made up of two or more geographically associated soils or
miscellaneous areas that are shown as one unit on the maps. Because of present
or anticipated uses of the map units in the survey area, it was not considered
practical or necessary to map the soils or miscellaneous areas separately. The
pattern and relative proportion of the soils or miscellaneous areas are somewhat
similar. Alpha-Beta association, 0 to 2 percent slopes, is an example.
An undifferentiated group is made up of two or more soils or miscellaneous areas
that could be mapped individually but are mapped as one unit because similar
interpretations can be made for use and management. The pattern and proportion
of the soils or miscellaneous areas in a mapped area are not uniform. An area can
be made up of only one of the major soils or miscellaneous areas, or it can be made
up of all of them. Alpha and Beta soils, 0 to 2 percent slopes, is an example.
Some surveys include miscellaneous areas. Such areas have little or no soil
material and support little or no vegetation. Rock outcrop is an example.
Custom Soil Resource Report
9
Hamilton County, Indiana
UkbB2—Urban land-Miami silt loam complex, 2 to 6 percent slopes,
eroded
Map Unit Setting
National map unit symbol: 2y47f
Elevation: 180 to 1,040 feet
Mean annual precipitation: 37 to 46 inches
Mean annual air temperature: 48 to 55 degrees F
Frost-free period: 145 to 180 days
Farmland classification: Not prime farmland
Map Unit Composition
Urban land:60 percent
Miami, eroded, and similar soils:30 percent
Minor components:10 percent
Estimates are based on observations, descriptions, and transects of the mapunit.
Description of Miami, Eroded
Setting
Landform:Till plains
Landform position (two-dimensional):Backslope, footslope, shoulder
Landform position (three-dimensional):Side slope
Down-slope shape:Convex
Across-slope shape:Linear
Parent material:Loess over loamy till
Typical profile
Ap - 0 to 8 inches: silt loam
Bt - 8 to 13 inches: silty clay loam
2Bt - 13 to 31 inches: clay loam
2BCt - 31 to 36 inches: loam
2Cd - 36 to 79 inches: loam
Properties and qualities
Slope:2 to 6 percent
Depth to restrictive feature:24 to 40 inches to densic material
Drainage class:Moderately well drained
Runoff class: High
Capacity of the most limiting layer to transmit water (Ksat):Low to moderately high
(0.01 to 0.20 in/hr)
Depth to water table:About 24 to 36 inches
Frequency of flooding:None
Frequency of ponding:None
Calcium carbonate, maximum content:45 percent
Maximum salinity:Nonsaline to very slightly saline (0.0 to 2.0 mmhos/cm)
Available water supply, 0 to 60 inches: Low (about 5.8 inches)
Interpretive groups
Land capability classification (irrigated): None specified
Land capability classification (nonirrigated): 2e
Hydrologic Soil Group: C
Ecological site: F111AY009IN - Till Ridge
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10
Other vegetative classification: Trees/Timber (Woody Vegetation)
Hydric soil rating: No
Minor Components
Crosby
Percent of map unit:5 percent
Landform:Till plains
Landform position (two-dimensional):Summit
Landform position (three-dimensional):Interfluve
Down-slope shape:Linear
Across-slope shape:Convex
Ecological site:F111AY008IN - Wet Till Ridge
Other vegetative classification:Trees/Timber (Woody Vegetation)
Hydric soil rating: No
Treaty
Percent of map unit:3 percent
Landform:Till plains
Landform position (two-dimensional):Toeslope
Landform position (three-dimensional):Dip
Down-slope shape:Concave
Across-slope shape:Concave
Ecological site:F111AY007IN - Till Depression Flatwood
Other vegetative classification:Mixed/Transitional (Mixed Native Vegetation)
Hydric soil rating: Yes
Williamstown
Percent of map unit:2 percent
Landform:Till plains
Landform position (two-dimensional):Shoulder, backslope
Landform position (three-dimensional):Side slope
Down-slope shape:Convex
Across-slope shape:Linear
Ecological site:F111AY009IN - Till Ridge
Other vegetative classification:Trees/Timber (Woody Vegetation)
Hydric soil rating: No
Custom Soil Resource Report
11
07/09/2021
Dimond Bros. Insurance, LLC
11708 North College Avenue
Carmel IN 46032
Laurie Kay
(317) 853-3572 (317) 853-3501
laurie.kay@dimondbros.com
Weihe Engineers, Inc.
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Indianapolis IN 46280
Continental Casualty Company 20443
21-22 Prof/Poll Master
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