SWPPP24154 043025 SS
site plan
101 pages
Meeting: portal event 1056 (no meeting page on file)
Agenda item: Old Busines — WBP Development, LLC - 1 Croton Point Avenue/ "Lot A" (79.17-1-5,4 &3) - Application for Site Plan Approval for Five-Story Building with 100 Dwelling Units and Subdivision Approval for Consolidation Subdivision
Site plan, 101 pages. Attached to agenda item: “Old Busines — WBP Development, LLC - 1 Croton Point Avenue/ "Lot A" (79.17-1-5,4 &3) - Application for Site Plan Approval for Five-Story Building with 100 Dwelling Units and Subdivision Approval for Consolidation Subdivi”
Retrieved 2026-04-15 from the village's meeting portal.
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Also attached to this agenda item:
2025-05-01 WBP Croton Point Full Set ss
250326 1CrotonPoint PlanningBoardIssue
Draft eNOI Croton Point
MS4
Response Letter 05012025CoHPB
Extracted text
STORMWATER POLLUTION PREVENTION PLAN
For
1 Croton Point
Croton Point Ave.
April 30, 2025
Applicant Information:
Note: This report in conjunction with the project plans make up the complete Stormwater
Pollution Prevention Plan.
PAGE
1.0
INTRODUCTION ............................................................................................................... 1
1.1 Project Description .................................................................................................... 1
1.2 Existing Site Conditions ............................................................................................ 1
1.3 Proposed Site Conditions .......................................................................................... 1
2.0
STORMWATER MANAGEMENT ................................................................................... 2p
2.1 NYSDEC Runoff Reduction Volume, RRv ................................................................. 4
2.2 NYSDEC Water Quality Volume, WQv ...................................................................... 4
2.3 NYSDEC Stream Channel Protection Volume, CPv ................................................. 5
2.4 NYSDEC Overbank Flood Control, Qp, and Extreme Flood Control, Qf ................... 6
3.0
STORMWATER CONVEYANCE SYSTEM ...................................................................... 6
4.0
EROSION AND SEDIMENT CONTROL .......................................................................... 6
4.1 Temporary Erosion and Sediment Control Facilities................................................. 7
4.2 Permanent Erosion and Sediment Control Facilities ................................................ 7
5.0
IMPLEMENTATION, MAINTENANCE & GENERAL HOUSEKEEPING ......................... 7
5.1 Construction Phase ................................................................................................... 7
5.2 Long Term Maintenance Plan ................................................................................... 9
APPENDICES
Appendix A
NYSDEC Water Quality Volume (WQv) Calculation Worksheets
Appendix B
Pre-Development Computer Data
Appendix C
Post-Development Computer Data
Appendix D
Project and Owner Information
Appendix E
NYSDEC SPDES General Permit for Construction Activities Construction Site Log
Book
Appendix F
Hydrodynamic Separator Sizing and Maintenance Information
Appendix G Pipe Sizing Calculations
Appendix H
OPRHP/SHPO Determination Letter
FIGURES
Figure 1: Location Map
Figure 2: Pre-Development Drainage Map
Figure 3: Post-Development Drainage Map
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1.0
INTRODUCTION
1.1
Project Description
The project consists of a proposed 100-unit, for sale affordable condominium development
consisting of 46 one-bedroom and 54 two-bedroom homes in a to be constructed 5-story building with
requisite parking and amenities (the “Development”) to be located on lands fronting on Croton Point
Avenue consisting of (i) Tax Map Parcels 79.17-1-5 & 3 owned by the Village (“Lot A”); and (ii) Tax
Map Parcel 79.17-1-3 owned by Croton Point Realty Inc (the “CPR Parcel”). Lot A is currently in use
as a Village commuter parking lot. The CPR Parcel is improved with an office building which is
proposed to be demolished for the Development.
The proposed brick and metal panel building will be served by 100 parking spaces to be
located in a below grade parking level and two outdoor parking areas, including five (5) Level 2 EV
charging stations. Amenities within the building will include a community room, a fitness center, a co-
working lounge, a bike storage room and a roof-top deck providing expansive scenic views
overlooking Croton Point Bay and the Hudson River.
Sustainable building design features will likely include full electrification, solar readiness, high
efficiency HVAC equipment (cold climate air source heat pumps) and appliances (Energy Star
Multifamily New Construction Program) and low-flow water fixtures.
In total the property consist of 1.8 ± acres and is located in the LI (Light Industrial with a
Transoriented Development Overlay) zoning district, the Village of Corton-on-Hudson Water District
and the Ossining Sanitary Sewer District.
1.2
Existing Site Conditions
The subject project is located on Croton Point Avenue across from Veterans Plaza in the
Village of Croton-On-Hudson. As previously stated, the site currently exists as a commercial
development with several buildings, parking areas, walkways, and other appurtenances. The
stormwater runoff from the existing property generally drains from a high point in the center of the
property north and south towards the existing drain inlets and their collection system, which discharge
to the west and east respectively. The northern drain inlet flows west onto MTA property and the
southern drain inlet flows east onto NYSDOT property.
The two drain inlets discussed above have been designed as Design Points for the purpose of
stormwater quantity analysis contained herein, and are shown on Figures 2 and 3. Design Point 1
represents the existing drainage structure at the corner of Croton Point Avenue and NYS Route 9 that
flows east. Design Point 2 represents the drainage structure that is part of the existing collection
system that discharges west towards the Metro North Railroad property.
Onsite soils belong to the Hydrologic Group B. Pursuant to the National Resource Conservation
Service Web Soil Survey, the soil designations of the onsite soils consist of Urban land (Uf) and
Udorthents (Ub). The soil boundaries are shown on the enclosed pre- and post-development
drainage figures, Figures 2 and 3 of this report.
It is proposed to construct a 21,500 sf ± (footprint area) affordable condominium with
associated parking and various site appurtenances. The new five-story building will contain one
hundred apartments. There will be 46 one-bedroom apartments and 54 two-bedroom apartments.
Amenity spaces will also be constructed which will be used by the residents of the building only.
This project is a redevelopment project with an overall decrease in impervious area. The
project results in a net decrease of 0.2 acres +/-.
It is proposed to maintain the overall drainage boundaries to the maximum extent practicable and
tie into the existing onsite collection system in the proposed condition. New drainage structures will
capture the runoff from the redeveloped site and will discharge into the hydrodynamic separators for
treatment of the new impervious areas. The intent is to capture and treat the stormwater runoff from the
redeveloped area of the site and treat it in accordance with the NYSDEC standards for quality and
quantity prior to discharging to the existing stormwater collection systems, such there is no impact to the
surrounding stormwater design. Two hydrodynamic separators are proposed in total, one tributary to
each design point.
As shown in the following sections of this report, the stormwater quality and quantity for the
proposed development have been treated in accordance with the requirements of the General Permit,
GP-0-25-001. Additionally, an erosion and sediment control plan has been prepared in accordance
with the New York State Standards and Specifications for Erosion and Sediment Control (Blue Book)
to protect the existing waterbodies and drainage features during construction activities.
Based on discussions with the owner, a Phase 1/Phase 2 study was completed for the site. Based
on the study, there is no known contamination or other restrictions on the property that would prevent
the normal discharge of the footings. The 2025 GCP defines dewatering as the act of draining
rainwater and/or groundwater from building foundations, vaults, or excavations / trenches. As the
footing drains are defined as dewatering operations and there is no knows contamination, it is
confirmed the footing drains meet the 2025 GCP definition for Uncontaminated discharges from
dewatering operations.
2.0
STORMWATER MANAGEMENT
The proposed stormwater management system for the project has been designed to meet the
requirements of the state stormwater ordinances and guidelines, including but not limited to those of the
NYSDEC.
As noted in Part III.A.2 of the General Permit GP-0-25-001, consideration of future physical risks due
to climate change pursuant to Community Risk and Resiliency Act (CRRA), 6 NYCRR Part 490 shall be
considered. First, the CRRA primarily focuses on areas subject to flooding and areas at risk of sea level rise.
The proposed project is not in an area for flood risk due to sea level rise and there are no FEMA regulated
Floodways or Floodplains on the subject property or within the surrounding vicinity. Additionally, there is no
immediate downstream infrastructure such as dams or major road culvert crossings that are potentially
impacted by the proposed project. There are no known flood issues that have occurred in or around the
project site. See below the current rainfall data obtained from the Northeast Regional Climate Center
(NRCC) and the Natural Resources Conservation Service (NRCS) utilized in this report. This rainfall data
which is updated annually allows designers to account for the most recent climate data recorded and allows
for site specific distribution curves to be utilized. Based on the foregoing, it is believed the requirements of
Part III.A.2 of General Permit GP-0-25-001 are addressed through this project SWPPP.
In accordance with the GP-0-25-001, Part III.B.2.b.iii., as the subject project SWPPP was submitted for
review as part of the Site Plan application to the Village of Croton-on-Hudson Planning Board prior to the
issuance of the GP-0-25-001 and was developed using the 2015 NYSDEC New York State Stormwater
Management Design Manual (Design Manual), the subject project may continue to design the post-
construction stormwater management practices in conformance with the performance criteria in the 2015
Design Manual.
Since the subject project proposes the disturbance of more than one (1) acre, coverage under the New
York State Department of Environmental Conservation (NYSDEC) SPDES General Permit No. GP-0-25-001
(General Permit) is required. Chapter 4 of the NYSSMDM specifies five design criteria that are Water Quality
Volume (WQv), Runoff Reduction Volume (RRv), Stream Channel Protection Volume (CPv), Overbank Flood
Control (Qp), and Extreme Storm Control (Qf). The first two of these requirements relates to treating water
quality, while the later pertain to stormwater quantity (peak flow) attenuation. As noted in previous sections of
this report, this project is a redevelopment project with an increase in impervious area. As such the RRv
requirements and CPv requirements are not required. Per Chapter 9, the proposed hydrodynamic separators
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have been designed as a flow through practice. As such, the flow through practices have been sized for the
peak rate of runoff from 100% of the WQv design storm, as defined Chapter 4 to treat the WQv in
accordance with the NYSSMDM.
To meet the above referenced requirements, the following post construction stormwater management
practices are proposed for the project:
Proposed SMP
ID
NYSSMDM Ch. 9 Design
Designation
NYSDEC Uniform Stormwater
Sizing Criteria Satisfied
HDS 1.1
Hydrodynamic Separator (Alt. Practice)
WQv
HDS 2.1
Hydrodynamic Separator (Alt. Practice)
WQv
Sizing calculations for the hydrodynamic separators have been provided in Appendix A. Information
regarding the sizing and maintenance of the proposed hydrodynamic separators can be in Appendix F. As
noted above the hydrodynamic separators result in treatment of the entire site and will be sized to treat the
WQv peak flow as required by Chapter 9.
To address stormwater quantity requirements of the NYSDEC, the “HydroCAD” Stormwater Modeling
System,” by HydroCAD Software Solutions LLC in Tamworth, New Hampshire, was used to model and
assess the peak stormwater flows for the subject project. HydroCAD is a computer aided design program for
modeling the hydrology and hydraulics of stormwater runoff. It is based primarily on hydrology techniques
developed by the United States Department of Agriculture, Soil Conservation Service (USDA, SCS) TR-20
method combined with standard hydraulic calculations. For details on the input data for the subcatchments
and design storms, please refer to Appendices B and C.
The input requirements for the HydroCAD computer program are as follows:
•
Design storm rainfall in inches
•
CN (runoff curve number) values which are based on soil type and land use/ground cover
•
Tc (time of concentration) flow path information
•
Watershed Area in Acres
Stormwater Basins
•
Surface area at appropriate elevations
•
Flood elevation
•
Outlet structure information
The following is a general description of the input data used to calculate the pre- and post-
development stormwater runoff values. For detailed information for each subcatchment and stormwater
management practice, see Appendices B & C. The 1-year, 10-year, and 100-year 24-hour design storm
were obtained from the New York State Stormwater Management Design Manual. The values provided are
for 24-hour design storms.
Table 2.0.1 – Precipitation Values for Corresponding Design Storms
Design Storm
24-Hour Rainfall
1.1S WQv Storm
1.87”
2.1S WQv Storm
1.66”
1-Year
2.34”
10-Year
4.66”
25-Year
6.50”
8.82”
The CN (runoff curve number) values utilized in this report were referenced from the USDA, SCS
publication Urban Hydrology for Small Watersheds. The following is a summary of the various land
uses/ground covers and their associated CN values utilized in this report.
Table 2.0.2 – Project Ground Cover and Associated Curve Numbers (CN)
2.1
NYSDEC Runoff Reduction Volume, RRv
The Runoff Reduction Volume (RRv) criterion is intended to replicate pre-development
hydrology by maintaining preconstruction infiltration, peak flow runoff, discharge volume, as well as
minimizing concentrated stormwater flow. As noted above, meeting the Runoff Reduction Volume
(RRv) sizing criteria is not required for redevelopment projects with a reduction in overall impervious
cover.
2.2
NYSDEC Water Quality Volume, WQv
The stormwater management practice has been designed in accordance with the Water Quality
Volume (WQv) Section (Chapter 4.2) of the NYSSMDM. As outlined in Chapter 4.2, the WQv is the
runoff volume generated from the entire 90th percentile rain event. As previously stated, partitions of
the proposed impervious surfaces will overlap existing impervious surfaces within the site area. Per
Section 9.2.1.B.III of the NYSSMDM, 100% WQv is captured and treated, for a minimum of 75% of
the disturbed redevelopment area. A calculation is provided below for the Total WQv required based
on Section 9.2.1.B.III of the NYSSMDM and included in Appendix A:
The water quality volume shall be WQv = (0.75) (P)(Rv)(A)
Where,
WQv
= water quality volume (in acre-feet)
P
= 90% Rainfall Event Number
Rv
= 0.05 + 0.009(I), where I is percent impervious cover
A = disturbed redeveloped area
Total WQv Required = 5,097 cf (See Calculation in Appendix A)
The proposed hydrodynamic separators (HDS 1.1 & HDS 2.1) have been designed as a flow
through practice, per Chapter 9 of the NYSSMDM. As such, the flow through alternative practices
have been sized for the peak rate of runoff from 100% of the WQv design storm, as defined Chapter
4 to treat the WQv in accordance with the NYSSMDM. In Appendix A of this report the calculation for
the WQv to be treated.
Table 2.2.1 below summarizes the WQv treatment and Required Elements for the proposed
Hydrodyanmic Separators (HDS 1.1 & HDS 2.1). The hydrodynamic separators have been designed
in accordance with the Chapter 9 of the Design Manual for an alternative practice. As shown on the
project plans, a Hydro-Shield Advance Hydrodynamic Separator by Oldcastle are proposed. The
Hydr-Shield Advance is an NJCAT verified proprietary practice. The table below summarizes the
required and provided WQv treatment rates. See Appendix A and F for more sizing information.
Subcatchment
ID
HDS ID
100%
WQv*
(C.F)
100%WQv
Peak Flow
(C.F.S)
Separator
Model
Maximum
Treatment
Flow Rate
(C.F.S.)
Peak
Flow
(C.F.S.)
25-Year
Peak Flow
(C.F.S)
1.1S
HDS 1.1
4,165
1.48
4-ft Hydro-Shield
1.49 CFS
7.4 CFS
5.06 CFS
2.1S
HDS 2.1
2,586
0.88
4-ft Hydro-Shield
1.49 CFS
7.4 CFS
2.89 CFS
* The total WQv required represents 75% of the WQv from onsite areas only. The 100% WQv from 1.1S &
2.1S if summed exceeds the total WQv required because it includes 100% of the volume not 75% and
includes offsite areas tributary to the practice.
Table 2.2.2 WQv Provided Summary
Total WQv Required
(C.F.)
Total WQv Provided
(C.F.)
5,097
6,751
It should be noted that the above tables illustrate the water quality volume requirements set
forth in the NYSSWDM have been met for the Hydrodynamic Separators (HDS 1.1 & HDS 2.1). By
meeting the Water Quality Volume requirements through employment of an alternative practice, the
water quality objectives of the NYSDEC to treat the water quality volume will be met.
2.3
NYSDEC Stream Channel Protection Volume, CPv
The Stream Channel Protection (CPv) criterion is intended to protect stream channels from
erosion and is accomplished by the 24-hour extended detention of the center-of-mass of the one-
year, 24-hour storm event. As per the NYSSWDM Chapter 9, if the post-construction 1-year 24 hour
discharge rate and velocities are less than or equal to the pre-construction design rate, providing 24
hours detention of the 1 year storm to meet CPv criteria is not required. Table 2.3.1 below
summarizes the peak flows discharging for the 1-Year 24-Hour design storm and demonstrates that
the 1-Year 24-Hour post development rate is less than the predevelopment rate.
Table 2.4.1– Pre and Post-Development Peak Flows at the Design Point
1-YEAR
(Channel Protection Volume)
Pre
Post
Design Point 1
3.0
2.6
Design Point 2
2.2
2.1
The data for the table above was taken from Appendix B & C of this SWPPP. As shown in the
table above the peak flows discharging to the design point have beem mitigated for the 1-Year 24-
Hour Storm. By providing a reduction in peak flows during the 1-Year, 24-hour storm, the NYSDEC
requirements for Stream Channel Protection (Cpv) have been met.
The Overbank Flood Control (Qp) requirement is intended to prevent an increase in the
frequency and magnitude of out-of-bank flooding events generated by urban development. Overbank
control requires storage to attenuate the post-development 10-year, 24-hour peak discharge to pre-
development rates. The Extreme Flood Control (Qf) requirement is intended to prevent the increased
risk of flood damage from large storm events, maintain the boundaries of the pre-development 100-
year flood plain, and protect the physical integrity of stormwater management practices. Extreme
flood control requires storage to attenuate the post-development 100-year, 24-hour peak discharge to
pre-development rates. As shown in Table 2.4.1 attenuation for both the 10-year and 100-year 24-
hour storms has been provided thus satisfying the Qp and Qf requirements.
Table 2.4.1– Pre and Post-Development Peak Flows at the Design Point
24-HOUR DESIGN STORM PEAK FLOWS (c.f.s.)
10-YEAR
(Overbank Flood Control)
Pre
Post
Pre
Post
Design Point 1
5.2
5.0
8.6
8.4
Design Point 2
4.8
4.7
8.9
8.8
As shown in the above table the peak flows discharging to the design point in the proposed
condition have been mitigated to below the existing condition levels, therefore the receiving
downstream drainage systems will see a reduction in peak flows during the storm events shown
above and as such satisfy the Overbank and Extreme Overbank Flood Control requirements.
3.0
STORMWATER CONVEYANCE SYSTEM
The stormwater collection and conveyance systems for the project will consist of catch basins, drain
inlets, yard drains, and HDPE pipe. The pipe conveyance system will be sized to collect and convey at
minimum the 25-year, 1-hour design storm using the Rational Method. The Rational Method is a standard
method used by engineers to develop flow rates for sizing collection systems. The Rational Method calculates
flows based on a one-hour design storm. See Appendix G for Pipe Sizing Calculations
4.0
EROSION AND SEDIMENT CONTROL
Erosion and sediment control should be accomplished by four basic principles: diversion of clean water,
containment of sediment, treatment of dirty water, and stabilization of disturbed areas. Diversion of clean
water should be accomplished with swales. This diverted water should be safely conveyed around the
construction area as necessary and discharged downstream of the disturbed areas. Sediment should be
contained with the use of silt fence at the toe of disturbed slopes and excavation of the temporary sediment
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basin. Disturbed areas should be permanently stabilized within 14 days of final grading to limit the required
length of time that the temporary facilities must be utilized. The owner will be responsible for the maintenance
of the temporary erosion control facilities.
4.1
Temporary Erosion and Sediment Control Facilities
Temporary erosion and sediment control facilities should be installed and maintained as required
to reduce the impacts to off-site properties. The owner will be required to provide maintenance for the
temporary erosion and sediment control facilities. In general, the following temporary methods and
materials should be used to control erosion and sedimentation from the project site:
A stabilized construction entrance should be installed at the entrance to the site. The design
drawings will include details to guide the contractor in the construction of this entrance. The intent of
the stabilized construction entrance is to prevent the “tracking” of soil from the site. Dust control should
be accomplished with water sprinkling trucks if required. During dry periods, sprinkler trucks should wet
all exposed earth surfaces as required to prevent the transport of air-borne particles to adjoining areas.
Siltation barriers constructed of geosynthetic filter cloth should be installed at the toe of all disturbed
slopes. The intent of these barriers is to contain silt and sediment at the source and inhibit its transport by
stormwater runoff. The siltation barriers will also help reduce the rate of runoff by creating filters through
which the stormwater must pass.
Storm drain inlet protection in the form of stone drop inlet protection will be installed around all
proposed inlets. The stone drop inlet protection will serve to filter stormwater runoff before it enters the
collection system. Throughout construction the concrete drainage structures, associated piping and inlet
protections shall be inspected weekly and after a rainfall event. These items shall be cleaned, repaired
and/or replaced when needed.
4.2
Permanent Erosion and Sediment Control Facilities
Permanent erosion and sediment control will be accomplished by diverting stormwater runoff
from steep slopes, controlling/reducing stormwater runoff velocities and volumes, and vegetative and
structural surface stabilization. All of the permanent facilities are relatively maintenance free and only
require periodic inspections. The owner will provide maintenance for all the permanent erosion and
sediment control facilities.
Other than the buildings and paved surfaces, disturbed surfaces will be stabilized with
vegetation. The vegetation will control stormwater runoff by preventing soil erosion, reducing runoff
volume and velocities, and providing a filter medium. Permanent seeding should optimally be
undertaken in the spring from March 21st through May 20th and in late summer from August 15th to
October 15th.
5.0
IMPLEMENTATION, MAINTENANCE & GENERAL HOUSEKEEPING
5.1
Construction Phase
Details associated with the implementation and maintenance of the proposed stormwater
facilities and erosion control measures during construction are shown on the project drawings. A
construction sequence has been provided to guide the contractor in the installation of the erosion
control measures as well as the site plan features. The erosion control plan, includes associated
details and notes to aid the contractor in implementing the plan.
During construction, a Site Log Book, Appendix E, is required to be kept per NYSDEC SPDES
General Permit GP-0-25-001. Erosion and sediment control inspections are required to be conducted
as necessary under coverage of the permit (minimum once a week, two times a week should the
overall disturbance exceed five acres) and an updated logbook and a copy of the SWPPP is required
to be kept on site for the duration of the construction activities. The Construction Site Log Book is an
appendix taken from the New York Standards and Specifications for Erosion and Sediment Control (Blue
Book).
In addition to the proposed erosion and sediment control facilities, the following good
housekeeping best management practices shall be implemented to mitigate potential pollution during
the construction phase of the project. The general contractor overseeing the day-to-day site operation
shall be responsible for the good housekeeping best management practices included in the following
general categories:
•
Material Handling and Waste Management
•
Establishment of Building Material Staging Areas
•
Establishment of Washout Areas
•
Proper Equipment Fueling and Maintenance Practices
•
Spill Prevention and Control Plan
All construction waste materials shall be collected and removed from the site regularly by the general
contractor. The general contractor shall supply waste barrels for proper disposal of waste materials. All
personnel working on the site shall be instructed of the proper procedures for construction waste disposal.
Although it is not anticipated any hazardous waste materials will be utilized during construction, any
hazardous waste materials shall be disposed of in accordance with federal, state, and local regulations. No
hazardous waste shall be disposed of on-site. Hazardous waste materials shall be stored in appropriate and
clearly marked containers and segregated from the other non-waste materials. All hazardous waste shall be
stored in structurally sound and sealed shipping containers located in the staging areas. Material safety data
sheets, material inventory, and emergency contact numbers will be maintained in the office trailer. All
personnel working on the site shall be instructed of the proper procedures for hazardous waste disposal.
Temporary sanitary facilities (portable toilets) shall be provided on site during the entire length of
construction. The sanitary facilities shall be located in an alternate area away from the construction activities
on the site. The portable toilets shall be inspected weekly for evidence of leaking holding tanks.
All recyclables, including wood pallets, cardboard boxes, and all other recyclable construction scraps
shall be disposed of in a designated recycling barrel provided by the contractor and removed from the site
regularly. All personnel working on the site shall be instructed of the proper procedures for construction
waste recycling.
All construction equipment and maintenance materials shall be stored in a designated staging area.
Silt fence shall be installed down gradient of the construction staging area. Shipping containers shall be
utilized to store hand tools, small parts, and other construction materials, not taken off site daily. Construction
waste barrels, recycling barrels and if necessary hazardous waste containers shall be located within the
limits of the construction staging area.
Throughout the construction of the project, several types of vehicles and equipment will be used on-
site. Fueling of the equipment shall occur within the limits of the construction staging area. Fuel will be
delivered to the site as needed, by the general contractor, or a party chosen by the general contractor. Only
minor vehicle equipment maintenance shall occur on-site, all major maintenance shall be performed off-site.
All equipment fluids generated from minor maintenance activities shall be disposed of into designated drums
and stored in accordance with the hazardous waste storage as previously discussed.
Vehicles and equipment shall be inspected on each day of use. Any leak discovered shall be repaired
immediately. All leaking equipment unable to be repaired shall be removed from the site. Ample supplies of
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absorbent, spill-cleanup materials, and spill kits shall be located in the construction staging area. All spills
shall be cleaned up immediately upon discovery. Spent absorbent materials and rags shall be hauled off-site
immediately after the spill is cleaned for disposal at a local landfill. All personnel working on the site shall be
instructed of the proper procedures for spill prevention and control.
During the construction phase of the project the subsurface infiltration system shall be cordoned off
with construction fence to prevent undue compaction of the surrounding soils. The infiltration areas shall not
be allowed to receive runoff until the contributing area to the system is completely stabilized in accordance
with the erosion and sediment control notes on the project drawings. Installation of the system after the
contributing area is stable will help to prevent any sediment from entering the SMP.
5.2
Long Term Maintenance Plan
Each spring the paved areas should be cleaned to remove the winter’s accumulation of traction
sand. After this is completed, all drain inlets sumps and the stormwater basins should be cleaned.
All pipes should be checked for debris and blockages and cleaned as required. During the cleaning
process, the drain inlets, catch basins, and pipes should be inspected for structural integrity and
overall condition; repairs and/or replacement will be made as required.
The stormwater facilities for the subject project have been designed to minimize the required
maintenance. This section discusses the minimum maintenance requirements to insure long-term
performance of the stormwater facilities. Initially the stormwater facilities will require an increased
maintenance and inspection schedule until all portions of the site are stable. Generally, the stormwater
facilities consist of either collection and conveyance components or treatment components.
The stormwater collection and conveyance system is composed of HDPE, drainage pipe and
precast concrete drainage structures. The owner will assume the maintenance responsibilities for the
drainage system. Minimal maintenance is typically required for these facilities. All pipes should be
checked for debris and blockages and cleaned as required. All drain inlet sumps shall be cleaned to
removed deposited sediment. During the cleaning process, the pipes should be inspected for structural
integrity and overall condition; repairs and/or replacement should be made as required.
Additionally, the hydrodynamic separators shall be checked for deposited sediment. Visual
inspection of the bioretention filter shall take place after major storm events. Visual inspection of the
hydrodynamic separator shall take place yearly.
NYSDEC Water Quality Volume WQv Calculations Worksheet
WQv Flow Calculation Worksheet
Project:
Date:
8/1/2024
The following calculation determines the water quality flow rate for the 90% Water Quality Event using the Small Storm
Hydrology Method specified in Appendix B of the New York State Stormwater Management Design Manual.
Total WQv Required
P = WQv 24-hour Rainfall Amount
=
1.5 in.
=
69696 SF
Ai= Impervious Area within Subcatchment Area
=
I = Ai/A
=
81.3 %
Rv = 0.05 + 0.009 (I%)
=
0.78
WQv = Water Quality Volume
=
5,097 CF
1.Water Quality Volume = = 0.75 ∗
∗
∗
Y:\Insite Forms\Design\Stormwater\WQv and WQv Peak Flow and Flow Splitter\WQv Vol and Peak Flow Calc.xls
WQv Flow Calculation Worksheet
Project:
Date:
5/1/2025
The following calculation determines the water quality flow rate for the 90% Water Quality Event using the Small Storm
Hydrology Method specified in Appendix B of the New York State Stormwater Management Design Manual.
HDS ID:
1.1S
P = WQv 24-hour Rainfall Amount
=
1.5 in.
=
39204 SF
Ai= Impervious Area within Subcatchment Area
=
I = Ai/A
=
88.9 %
Rv = 0.05 + 0.009 (I%)
=
0.85
WQv = Water Quality Volume
=
4,165 CF
The WQv Peak flow is determined using HydroCAD. However, the rainfall depth (P90) Value utilized is determined from the calculation below:
P90 = Calculated rainfall value (in)
CNw = Weighted Curve Number
=
S = Maximum basin retention (in)
S= (1000/CNw) - 10
=
0.64
Q = runoff generator over contributing area [Q = WQv/A]
=
1.27
=
1.86 in
1.Water Quality Volume =
2.Water Quality Peak Flow
= ∗ ∗
P90 =
.
(.
).
Y:\Insite Forms\Design\Stormwater\WQv and WQv Peak Flow and Flow Splitter\WQv Vol and Peak Flow Calc.xls
WQv Flow Calculation Worksheet
Project:
Date:
8/1/2024
The following calculation determines the water quality flow rate for the 90% Water Quality Event using the Small Storm
Hydrology Method specified in Appendix B of the New York State Stormwater Management Design Manual.
HDS ID:
2.1S
P = WQv 24-hour Rainfall Amount
=
1.5 in.
=
21780 SF
Ai= Impervious Area within Subcatchment Area
=
I = Ai/A
=
100.0 %
Rv = 0.05 + 0.009 (I%)
=
0.95
WQv = Water Quality Volume
=
2,586 CF
The WQv Peak flow is determined using HydroCAD. However, the rainfall depth (P90) Value utilized is determined from the calculation below:
P90 = Calculated rainfall value (in)
=
CNw = Weighted Curve Number
=
S = Maximum basin retention (in)
S= (1000/CNw) - 10
=
0.2041
Q = runoff generator over contributing area [Q = WQv/A]
=
1.4250
=
1.65
1.Water Quality Volume =
2.Water Quality Peak Flow
= ∗ ∗
P90 =
.+(6.252+25).
Y:\Insite Forms\Design\Stormwater\WQv and WQv Peak Flow and Flow Splitter\WQv Vol and Peak Flow Calc.xls
NY - Croton Point 24-hr S1 1-yr WQV 1.1 Rainfall=1.86"
App A - WQvt - Croton Point
Printed 5/1/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 1.1S: WQV
Runoff
=
1.48 cfs @ 12.04 hrs, Volume=
0.095 af, Depth= 1.27"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 1-yr WQV 1.1 Rainfall=1.86"
CN
Description
*
0.800
Impervious
0.100
>75% Grass cover, Good, HSG B
0.900
Weighted Average
0.100
11.11% Pervious Area
0.800
88.89% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
6.0
Direct Entry,
Subcatchment 1.1S: WQV
Runoff
Hydrograph
Time (hours)
WQV 1.1 Rainfall=1.86"
Runoff Area=0.900 ac
Runoff Volume=0.095 af
Runoff Depth=1.27"
Tc=6.0 min
CN=94
1.48 cfs
NY - Croton Point 24-hr S1 25-yr Rainfall=6.50"
App A - WQvt - Croton Point
Printed 5/1/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 1.1S: WQV
Runoff
=
5.06 cfs @ 12.04 hrs, Volume=
0.434 af, Depth= 5.79"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 25-yr Rainfall=6.50"
CN
Description
*
0.800
Impervious
0.100
>75% Grass cover, Good, HSG B
0.900
Weighted Average
0.100
11.11% Pervious Area
0.800
88.89% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
6.0
Direct Entry,
Subcatchment 1.1S: WQV
Runoff
Hydrograph
Time (hours)
NY - Croton Point 24-hr S1 25-yr
Rainfall=6.50"
Runoff Area=0.900 ac
Runoff Volume=0.434 af
Runoff Depth=5.79"
Tc=6.0 min
CN=94
5.06 cfs
NY - Croton Point 24-hr S1 1-yr WQV 2.1 Rainfall=1.65"
App A - WQvt - Croton Point
Printed 4/30/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 2.1S: WQv
Runoff
=
0.88 cfs @ 12.04 hrs, Volume=
0.060 af, Depth= 1.43"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 1-yr WQV 2.1 Rainfall=1.65"
CN
Description
*
0.500
Impervious
0.500
100.00% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
6.0
Direct Entry,
Subcatchment 2.1S: WQv
Runoff
Hydrograph
Time (hours)
0.95
0.9
0.85
0.8
0.75
0.7
0.65
0.6
0.55
0.5
0.45
0.4
0.35
0.3
0.25
0.2
0.15
0.1
0.05
NY - Croton Point 24-hr S1 1-yr
WQV 2.1 Rainfall=1.65"
Runoff Area=0.500 ac
Runoff Volume=0.060 af
Runoff Depth=1.43"
Tc=6.0 min
CN=98
0.88 cfs
NY - Croton Point 24-hr S1 25-yr Rainfall=6.50"
App A - WQvt - Croton Point
Printed 4/30/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 2.1S: WQv
Runoff
=
2.89 cfs @ 12.04 hrs, Volume=
0.261 af, Depth= 6.26"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 25-yr Rainfall=6.50"
CN
Description
*
0.500
Impervious
0.500
100.00% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
6.0
Direct Entry,
Subcatchment 2.1S: WQv
Runoff
Hydrograph
Time (hours)
NY - Croton Point 24-hr S1 25-yr
Rainfall=6.50"
Runoff Area=0.500 ac
Runoff Volume=0.261 af
Runoff Depth=6.26"
Tc=6.0 min
CN=98
2.89 cfs
1 Croton Point — SWPPP
SWPPP24154.doc
Insite Engineering, Surveying & Landscape Architecture, P.C.
PRE 1
PRE 2
Routing Diagram for App B - Pre Development - Croton Point
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C., Printed 7/31/2024
HydroCAD® 10.00-15 s/n 00891 © 2015 HydroCAD Software Solutions LLC
Subcat
Reach
Pond
Link
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
=
3.0 cfs @ 12.17 hrs, Volume=
0.285 af, Depth= 2.14"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
CN
Description
0.100
>75% Grass cover, Good, HSG B
1.450
Paved parking, HSG D
0.050
Woods, Good, HSG B
1.600
Weighted Average
0.150
9.38% Pervious Area
1.450
90.63% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
14.5
0.0500
0.11
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
1.6
0.0300
0.87
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
16.1
Total
Subcatchment PRE 1:
Runoff
Hydrograph
Time (hours)
CN=94
3.0 cfs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
=
2.2 cfs @ 12.12 hrs, Volume=
0.178 af, Depth= 1.34"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
CN
Description
0.100
>75% Grass cover, Good, HSG D
0.150
Woods, Good, HSG D
0.250
>75% Grass cover, Good, HSG B
0.200
Woods, Good, HSG B
0.900
Paved parking, HSG D
1.600
Weighted Average
0.700
43.75% Pervious Area
0.900
56.25% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
5.3
0.1000
0.13
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
3.8
0.0700
0.26
Sheet Flow,
Grass: Short n= 0.150 P2= 3.37"
0.4
0.0500
1.57
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
1.5
0.0400
1.00
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
0.4
0.2100
3.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.5
0.0100
2.03
Shallow Concentrated Flow,
Paved Kv= 20.3 fps
0.0
0.2000
25.50
31.30
Pipe Channel,
15.0" Round Area= 1.2 sf Perim= 3.9' r= 0.31'
n= 0.012
11.9
Total
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.178 af
Runoff Depth=1.34"
Flow Length=385'
Tc=11.9 min
CN=84
2.2 cfs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
=
5.2 cfs @ 12.17 hrs, Volume=
0.592 af, Depth= 4.44"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
CN
Description
0.100
>75% Grass cover, Good, HSG B
1.450
Paved parking, HSG D
0.050
Woods, Good, HSG B
1.600
Weighted Average
0.150
9.38% Pervious Area
1.450
90.63% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
14.5
0.0500
0.11
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
1.6
0.0300
0.87
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
16.1
Total
Subcatchment PRE 1:
Runoff
Hydrograph
Time (hours)
CN=94
5.2 cfs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
=
4.8 cfs @ 12.12 hrs, Volume=
0.452 af, Depth= 3.39"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
CN
Description
0.100
>75% Grass cover, Good, HSG D
0.150
Woods, Good, HSG D
0.250
>75% Grass cover, Good, HSG B
0.200
Woods, Good, HSG B
0.900
Paved parking, HSG D
1.600
Weighted Average
0.700
43.75% Pervious Area
0.900
56.25% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
5.3
0.1000
0.13
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
3.8
0.0700
0.26
Sheet Flow,
Grass: Short n= 0.150 P2= 3.37"
0.4
0.0500
1.57
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
1.5
0.0400
1.00
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
0.4
0.2100
3.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.5
0.0100
2.03
Shallow Concentrated Flow,
Paved Kv= 20.3 fps
0.0
0.2000
25.50
31.30
Pipe Channel,
15.0" Round Area= 1.2 sf Perim= 3.9' r= 0.31'
n= 0.012
11.9
Total
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.452 af
Runoff Depth=3.39"
Flow Length=385'
Tc=11.9 min
CN=84
4.8 cfs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
=
8.6 cfs @ 12.17 hrs, Volume=
1.143 af, Depth= 8.58"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
CN
Description
0.100
>75% Grass cover, Good, HSG B
1.450
Paved parking, HSG D
0.050
Woods, Good, HSG B
1.600
Weighted Average
0.150
9.38% Pervious Area
1.450
90.63% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
14.5
0.0500
0.11
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
1.6
0.0300
0.87
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
16.1
Total
Subcatchment PRE 1:
Runoff
Hydrograph
Time (hours)
CN=94
8.6 cfs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
=
8.9 cfs @ 12.11 hrs, Volume=
0.980 af, Depth= 7.35"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
CN
Description
0.100
>75% Grass cover, Good, HSG D
0.150
Woods, Good, HSG D
0.250
>75% Grass cover, Good, HSG B
0.200
Woods, Good, HSG B
0.900
Paved parking, HSG D
1.600
Weighted Average
0.700
43.75% Pervious Area
0.900
56.25% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
5.3
0.1000
0.13
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
3.8
0.0700
0.26
Sheet Flow,
Grass: Short n= 0.150 P2= 3.37"
0.4
0.0500
1.57
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
1.5
0.0400
1.00
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
0.4
0.2100
3.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.5
0.0100
2.03
Shallow Concentrated Flow,
Paved Kv= 20.3 fps
0.0
0.2000
25.50
31.30
Pipe Channel,
15.0" Round Area= 1.2 sf Perim= 3.9' r= 0.31'
n= 0.012
11.9
Total
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 7/31/2024
Prepared by Insite Engineering, Surveying and Landscape Architecture, P.C.
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.980 af
Runoff Depth=7.35"
Flow Length=385'
Tc=11.9 min
CN=84
8.9 cfs
1 Croton Point — SWPPP
SWPPP24154.doc
Insite Engineering, Surveying & Landscape Architecture, P.C.
1.0S & 1.1S
2.0S & 2.1S
DP 1
DESIGN POINT 1
DP 2
DESIGN POINT 2
Routing Diagram for App C - Post Development - Croton Point
Prepared by {enter your company name here}, Printed 3/26/2025
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Subcat
Reach
Pond
Link
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 1.0S & 1.1S:
Runoff
=
2.6 cfs @ 12.17 hrs, Volume=
0.249 af, Depth= 1.87"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
CN
Description
0.250
>75% Grass cover, Good, HSG B
0.050
Woods, Good, HSG B
1.300
Paved parking, HSG D
1.600
Weighted Average
0.300
18.75% Pervious Area
1.300
81.25% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
14.5
0.0500
0.11
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
1.6
0.0300
0.87
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
16.1
Total
Subcatchment 1.0S & 1.1S:
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.249 af
Runoff Depth=1.87"
CN=91
2.6 cfs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 2.0S & 2.1S:
Runoff
=
2.1 cfs @ 12.12 hrs, Volume=
0.170 af, Depth= 1.27"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
CN
Description
0.150
>75% Grass cover, Good, HSG D
0.100
Woods, Good, HSG D
0.300
>75% Grass cover, Good, HSG B
0.200
Woods, Good, HSG B
0.850
Paved parking, HSG D
1.600
Weighted Average
0.750
46.88% Pervious Area
0.850
53.13% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
5.3
0.1000
0.13
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
3.8
0.0700
0.26
Sheet Flow,
Grass: Short n= 0.150 P2= 3.37"
0.4
0.0500
1.57
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
1.5
0.0400
1.00
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
0.4
0.2100
3.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.2
0.1000
2.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.2
0.0150
2.49
Shallow Concentrated Flow,
Paved Kv= 20.3 fps
0.1
0.0010
1.80
2.21
Pipe Channel,
15.0" Round Area= 1.2 sf Perim= 3.9' r= 0.31'
n= 0.012
11.9
Total
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Subcatchment 2.0S & 2.1S:
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.170 af
Runoff Depth=1.27"
Flow Length=374'
Tc=11.9 min
CN=83
2.1 cfs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Reach DP 1: DESIGN POINT 1
Inflow Area =
1.600 ac, 81.25% Impervious, Inflow Depth = 1.87" for 1-yr event
Inflow
=
2.6 cfs @ 12.17 hrs, Volume=
0.249 af
Outflow
=
2.6 cfs @ 12.17 hrs, Volume=
0.249 af, Atten= 0%, Lag= 0.0 min
Routing by Dyn-Stor-Ind method, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
Reach DP 1: DESIGN POINT 1
Inflow
Outflow
Hydrograph
Time (hours)
2.6 cfs
2.6 cfs
NY - Croton Point 24-hr S1 1-yr Rainfall=2.78"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Reach DP 2: DESIGN POINT 2
Inflow Area =
1.600 ac, 53.13% Impervious, Inflow Depth = 1.27" for 1-yr event
Inflow
=
2.1 cfs @ 12.12 hrs, Volume=
0.170 af
Outflow
=
2.1 cfs @ 12.12 hrs, Volume=
0.170 af, Atten= 0%, Lag= 0.0 min
Routing by Dyn-Stor-Ind method, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
Reach DP 2: DESIGN POINT 2
Inflow
Outflow
Hydrograph
Time (hours)
2.1 cfs
2.1 cfs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 1.0S & 1.1S:
Runoff
=
5.0 cfs @ 12.17 hrs, Volume=
0.548 af, Depth= 4.11"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
CN
Description
0.250
>75% Grass cover, Good, HSG B
0.050
Woods, Good, HSG B
1.300
Paved parking, HSG D
1.600
Weighted Average
0.300
18.75% Pervious Area
1.300
81.25% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
14.5
0.0500
0.11
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
1.6
0.0300
0.87
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
16.1
Total
Subcatchment 1.0S & 1.1S:
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.548 af
Runoff Depth=4.11"
CN=91
5.0 cfs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 2.0S & 2.1S:
Runoff
=
4.7 cfs @ 12.12 hrs, Volume=
0.439 af, Depth= 3.29"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
CN
Description
0.150
>75% Grass cover, Good, HSG D
0.100
Woods, Good, HSG D
0.300
>75% Grass cover, Good, HSG B
0.200
Woods, Good, HSG B
0.850
Paved parking, HSG D
1.600
Weighted Average
0.750
46.88% Pervious Area
0.850
53.13% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
5.3
0.1000
0.13
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
3.8
0.0700
0.26
Sheet Flow,
Grass: Short n= 0.150 P2= 3.37"
0.4
0.0500
1.57
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
1.5
0.0400
1.00
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
0.4
0.2100
3.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.2
0.1000
2.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.2
0.0150
2.49
Shallow Concentrated Flow,
Paved Kv= 20.3 fps
0.1
0.0010
1.80
2.21
Pipe Channel,
15.0" Round Area= 1.2 sf Perim= 3.9' r= 0.31'
n= 0.012
11.9
Total
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Subcatchment 2.0S & 2.1S:
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.439 af
Runoff Depth=3.29"
Flow Length=374'
Tc=11.9 min
CN=83
4.7 cfs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Reach DP 1: DESIGN POINT 1
Inflow Area =
1.600 ac, 81.25% Impervious, Inflow Depth = 4.11" for 10-yr event
Inflow
=
5.0 cfs @ 12.17 hrs, Volume=
0.548 af
Outflow
=
5.0 cfs @ 12.17 hrs, Volume=
0.548 af, Atten= 0%, Lag= 0.0 min
Routing by Dyn-Stor-Ind method, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
Reach DP 1: DESIGN POINT 1
Inflow
Outflow
Hydrograph
Time (hours)
5.0 cfs
5.0 cfs
NY - Croton Point 24-hr S1 10-yr Rainfall=5.13"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Reach DP 2: DESIGN POINT 2
Inflow Area =
1.600 ac, 53.13% Impervious, Inflow Depth = 3.29" for 10-yr event
Inflow
=
4.7 cfs @ 12.12 hrs, Volume=
0.439 af
Outflow
=
4.7 cfs @ 12.12 hrs, Volume=
0.439 af, Atten= 0%, Lag= 0.0 min
Routing by Dyn-Stor-Ind method, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
Reach DP 2: DESIGN POINT 2
Inflow
Outflow
Hydrograph
Time (hours)
4.7 cfs
4.7 cfs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 1.0S & 1.1S:
Runoff
=
8.4 cfs @ 12.17 hrs, Volume=
1.095 af, Depth= 8.21"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
CN
Description
0.250
>75% Grass cover, Good, HSG B
0.050
Woods, Good, HSG B
1.300
Paved parking, HSG D
1.600
Weighted Average
0.300
18.75% Pervious Area
1.300
81.25% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
14.5
0.0500
0.11
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
1.6
0.0300
0.87
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
16.1
Total
Subcatchment 1.0S & 1.1S:
Runoff
Hydrograph
Time (hours)
Runoff Volume=1.095 af
Runoff Depth=8.21"
CN=91
8.4 cfs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Subcatchment 2.0S & 2.1S:
Runoff
=
8.8 cfs @ 12.11 hrs, Volume=
0.963 af, Depth= 7.23"
Runoff by SCS TR-20 method, UH=SCS, Weighted-CN, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
CN
Description
0.150
>75% Grass cover, Good, HSG D
0.100
Woods, Good, HSG D
0.300
>75% Grass cover, Good, HSG B
0.200
Woods, Good, HSG B
0.850
Paved parking, HSG D
1.600
Weighted Average
0.750
46.88% Pervious Area
0.850
53.13% Impervious Area
Tc
Length
Slope
Velocity
Capacity
Description
(min)
(feet)
(ft/ft)
(cfs)
5.3
0.1000
0.13
Sheet Flow,
Woods: Light underbrush n= 0.400 P2= 3.37"
3.8
0.0700
0.26
Sheet Flow,
Grass: Short n= 0.150 P2= 3.37"
0.4
0.0500
1.57
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
1.5
0.0400
1.00
Shallow Concentrated Flow,
Woodland Kv= 5.0 fps
0.4
0.2100
3.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.2
0.1000
2.21
Shallow Concentrated Flow,
Short Grass Pasture Kv= 7.0 fps
0.2
0.0150
2.49
Shallow Concentrated Flow,
Paved Kv= 20.3 fps
0.1
0.0010
1.80
2.21
Pipe Channel,
15.0" Round Area= 1.2 sf Perim= 3.9' r= 0.31'
n= 0.012
11.9
Total
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Subcatchment 2.0S & 2.1S:
Runoff
Hydrograph
Time (hours)
Runoff Volume=0.963 af
Runoff Depth=7.23"
Flow Length=374'
Tc=11.9 min
CN=83
8.8 cfs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Reach DP 1: DESIGN POINT 1
Inflow Area =
1.600 ac, 81.25% Impervious, Inflow Depth = 8.21" for 100-yr event
Inflow
=
8.4 cfs @ 12.17 hrs, Volume=
1.095 af
Outflow
=
8.4 cfs @ 12.17 hrs, Volume=
1.095 af, Atten= 0%, Lag= 0.0 min
Routing by Dyn-Stor-Ind method, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
Reach DP 1: DESIGN POINT 1
Inflow
Outflow
Hydrograph
Time (hours)
8.4 cfs
8.4 cfs
NY - Croton Point 24-hr S1 100-yr Rainfall=9.30"
Printed 3/26/2025
Prepared by {enter your company name here}
HydroCAD® 10.00-15 s/n 02171 © 2015 HydroCAD Software Solutions LLC
Summary for Reach DP 2: DESIGN POINT 2
Inflow Area =
1.600 ac, 53.13% Impervious, Inflow Depth = 7.23" for 100-yr event
Inflow
=
8.8 cfs @ 12.11 hrs, Volume=
0.963 af
Outflow
=
8.8 cfs @ 12.11 hrs, Volume=
0.963 af, Atten= 0%, Lag= 0.0 min
Routing by Dyn-Stor-Ind method, Time Span= 0.00-120.00 hrs, dt= 0.05 hrs
Reach DP 2: DESIGN POINT 2
Inflow
Outflow
Hydrograph
Time (hours)
8.8 cfs
8.8 cfs
1 Croton Point — SWPPP
SWPPP24154.doc
Insite Engineering, Surveying & Landscape Architecture, P.C.
Party Responsible for Implementation of the Stormwater Pollution Prevention Plan:
Qualified Professional Responsible for Inspection of the Stormwater Pollution Prevention Plan:
Inspector to be determined at time of construction
1 Croton Point — SWPPP
SWPPP24154.doc
Insite Engineering, Surveying & Landscape Architecture, P.C.
NYSDEC SPDES General Permit for Construction Activities Construction Site Log Book
November 2016
Page F.1 New York State Standards and Specifications
For Erosion and Sediment Control
STATE POLLUTANT DISCHARGE ELIMINATION SYSTEM FOR CONSTRUCTION
ACTIVITIES
SAMPLE CONSTRUCTION SITE LOG BOOK
Table of Contents
I. Pre-Construction Meeting Documents
a. Preamble to Site Assessment and Inspections
b. Pre-Construction Site Assessment Checklist
II. Construction Duration Inspections
a. Directions
b. Modification to the SWPPP
APPENDIX F
CONSTRUCTION SITE INSPECTION
AND MAINTENANCE LOG BOOK
November 2016
Page F.2
New York State Standards and Specifications
For Erosion and Sediment Control
I.
The Following Information To Be Read By All Person’s Involved in The Construction of Stormwater Re-
lated Activities:
The Operator agrees to have a qualified inspector1 conduct an assessment of the site prior to the commence-
ment of construction2 and certify in this inspection report that the appropriate erosion and sediment controls
described in the SWPPP have been adequately installed or implemented to ensure overall preparedness of
the site for the commencement of construction.
Prior to the commencement of construction, the Operator shall certify in this site logbook that the SWPPP
has been prepared in accordance with the State’s standards and meets all Federal, State and local erosion
and sediment control requirements. A preconstruction meeting should be held to review all of the SWPPP
requirements with construction personnel.
When construction starts, site inspections shall be conducted by the qualified inspector at least every 7 cal-
endar days. The Operator shall maintain a record of all inspection reports in this site logbook. The site log-
book shall be maintained on site and be made available to the permitting authorities upon request.
Prior to filing the Notice of Termination or the end of permit term, the Operator shall have a qualified in-
spector perform a final site inspection. The qualified inspector shall certify that the site has undergone final
stabilization3 using either vegetative or structural stabilization methods and that all temporary erosion and
sediment controls (such as silt fencing) not needed for long-term erosion control have been removed. In
addition, the Operator must identify and certify that all permanent structures described in the SWPPP have
been constructed and provide the owner(s) with an operation and maintenance plan that ensures the struc-
ture(s) continuously functions as designed.
1 Refer to “Qualified Inspector” inspection requirements in the current SPDES General Permit for Stormwater Discharges
from Construction Activity for complete list of inspection requirements.
2 “Commencement of construction” means the initial removal of vegetation and disturbance of soils associated with
clearing, grading or excavating activities or other construction activities.
3 “Final stabilization” means that all soil-disturbing activities at the site have been completed and a uniform, perennial
vegetative cover with a density of eighty (80) percent has been established or equivalent stabilization measures (such as
the use of mulches or geotextiles) have been employed on all unpaved areas and areas not covered by permanent struc-
tures.
1. Notice of Intent, SWPPP, and Contractors Certification:
[ ] [ ] [ ] Has a Notice of Intent been filed with the NYS Department of Conservation?
[ ] [ ] [ ] Is the Plan current? What is the latest revision date?______________
[ ] [ ] [ ] Is a copy of the NOI (with brief description) onsite? Where?______________
[ ] [ ] [ ] Have all contractors involved with stormwater related activities signed a contractor’s certification?
[ ] [ ] [ ] Are construction limits clearly flagged or fenced?
[ ] [ ] [ ] Important trees and associated rooting zones, on-site septic system absorption fields, existing
vegetated areas suitable for filter strips, especially in perimeter areas, have been flagged for
protection.
[ ] [ ] [ ] Creek crossings installed prior to land-disturbing activity, including clearing and blasting.
[ ] [ ] [ ] Clean stormwater runoff has been diverted from areas to be disturbed.
[ ] [ ] [ ] Bodies of water located either on site or in the vicinity of the site have been identified and protected.
[ ] [ ] [ ] Appropriate practices to protect on-site or downstream surface water are installed.
[ ] [ ] [ ] Are clearing and grading operations divided into areas <5 acres?
[ ] [ ] [ ] A temporary construction entrance to capture mud and debris from construction vehicles before they
enter the public highway has been installed.
[ ] [ ] [ ] Other access areas (entrances, construction routes, equipment parking areas) are stabilized
immediately as work takes place with gravel or other cover.
[ ] [ ] [ ] Sediment tracked onto public streets is removed or cleaned on a regular basis.
[ ] [ ] [ ] Silt fence material and installation comply with the standard drawing and specifications.
[ ] [ ] [ ] Silt fences are installed at appropriate spacing intervals
[ ] [ ] [ ] Sediment/detention basin was installed as first land disturbing activity.
[ ] [ ] [ ] Sediment traps and barriers are installed.
6. Pollution Prevention for Waste and Hazardous Materials
Yes No NA
[ ] [ ] [ ] The Operator or designated representative has been assigned to implement the spill prevention
avoidance and response plan.
[ ] [ ] [ ] The plan is contained in the SWPPP on page ______
[ ] [ ] [ ] Appropriate materials to control spills are onsite. Where? __________________
November 2016
Page F.4
New York State Standards and Specifications
For Erosion and Sediment Control
II. CONSTRUCTION DURATION INSPECTIONS
a. Directions:
Inspection Forms will be filled out during the entire construction phase of the project.
1) On a site map, indicate the extent of all disturbed site areas and drainage pathways. Indicate site
areas that are expected to undergo initial disturbance or significant site work within the next 14-day
period;
2) Indicate on a site map all areas of the site that have undergone temporary or permanent
stabilization;
3) Indicate all disturbed site areas that have not undergone active site work during the previous 14-day
period;
4) Inspect all sediment control practices and record the approximate degree of sediment accumulation
as a percentage of sediment storage volume (for example, 10 percent, 20 percent, 50 percent);
5) Inspect all erosion and sediment control practices and record all maintenance requirements such as
verifying the integrity of barrier or diversion systems (earthen berms or silt fencing) and
containment systems (sediment basins and sediment traps). Identify any evidence of rill or gully
erosion occurring on slopes and any loss of stabilizing vegetation or seeding/mulching. Document
any excessive deposition of sediment or ponding water along barrier or diversion systems. Record
the depth of sediment within containment structures, any erosion near outlet and overflow
structures, and verify the ability of rock filters around perforated riser pipes to pass water; and
6) Immediately report to the Operator any deficiencies that are identified with the implementation of
the SWPPP.
The above signed acknowledges that, to the best of his/her knowledge, all information provided on the
forms is accurate and complete.
[ ] [ ] [ ] Is there an increase in turbidity causing a substantial visible contrast to natural conditions at the
outfalls?
[ ] [ ] [ ] Is there residue from oil and floating substances, visible oil film, or globules or grease at the
outfalls?
[ ] [ ] [ ] All disturbance is within the limits of the approved plans.
[ ] [ ] [ ] Have receiving lake/bay, stream, and/or wetland been impacted by silt from project?
[ ] [ ] [ ] Is construction site litter, debris and spoils appropriately managed?
[ ] [ ] [ ] Are facilities and equipment necessary for implementation of erosion and sediment control in
working order and/or properly maintained?
[ ] [ ] [ ] Is construction impacting the adjacent property?
[ ] [ ] [ ] Is dust adequately controlled?
[ ] [ ] [ ] Maximum diameter pipes necessary to span creek without dredging are installed.
[ ] [ ] [ ] Installed non-woven geotextile fabric beneath approaches.
[ ] [ ] [ ] Is fill composed of aggregate (no earth or soil)?
[ ] [ ] [ ] Rock on approaches is clean enough to remove mud from vehicles & prevent sediment from
entering stream during high flow.
[ ] [ ] [ ] Stone is clean enough to effectively remove mud from vehicles.
[ ] [ ] [ ] Installed per standards and specifications?
[ ] [ ] [ ] Does all traffic use the stabilized entrance to enter and leave site?
[ ] [ ] [ ] Is adequate drainage provided to prevent ponding at entrance?
[ ] [ ] [ ] Upstream and downstream berms (sandbags, inflatable dams, etc.) are installed per plan.
[ ] [ ] [ ] Clean water from upstream pool is being pumped to the downstream pool.
[ ] [ ] [ ] Sediment laden water from work area is being discharged to a silt-trapping device.
[ ] [ ] [ ] Constructed upstream berm with one-foot minimum freeboard.
[ ] [ ] [ ] Installed per plan.
[ ] [ ] [ ] Constructed on undisturbed soil, not on fill, receiving only clear, non-sediment laden flow.
[ ] [ ] [ ] Flow sheets out of level spreader without erosion on downstream edge.
[ ] [ ] [ ] Installed per plan with minimum side slopes 2H:1V or flatter.
[ ] [ ] [ ] Stabilized by geotextile fabric, seed, or mulch with no erosion occurring.
[ ] [ ] [ ] Sediment-laden runoff directed to sediment trapping structure
4. Stone Check Dam
Yes No NA
[ ] [ ] [ ] Is channel stable? (flow is not eroding soil underneath or around the structure).
[ ] [ ] [ ] Check is in good condition (rocks in place and no permanent pools behind the structure).
[ ] [ ] [ ] Has accumulated sediment been removed?.
[ ] [ ] [ ] Installed per plan.
[ ] [ ] [ ] Installed concurrently with pipe installation.
[ ] [ ] [ ] Stockpiles are stabilized with vegetation and/or mulch.
[ ] [ ] [ ] Sediment control is installed at the toe of the slope.
[ ] [ ] [ ] Temporary seedings and mulch have been applied to idle areas.
[ ] [ ] [ ] 4 inches minimum of topsoil has been applied under permanent seedings
Sediment Control Practices
1. Silt Fence and Linear Barriers
Yes No NA
[ ] [ ] [ ] Installed on Contour, 10 feet from toe of slope (not across conveyance channels).
[ ] [ ] [ ] Joints constructed by wrapping the two ends together for continuous support.
[ ] [ ] [ ] Fabric buried 6 inches minimum.
[ ] [ ] [ ] Posts are stable, fabric is tight and without rips or frayed areas.
2. Storm Drain Inlet Protection (Use for Stone & Block; Filter Fabric; Curb; or, Excavated; Filter Sock or
Manufactured practices)
[ ] [ ] [ ] Installed concrete blocks lengthwise so open ends face outward, not upward.
[ ] [ ] [ ] Placed wire screen between No. 3 crushed stone and concrete blocks.
[ ] [ ] [ ] Drainage area is 1acre or less.
[ ] [ ] [ ] Excavated area is 900 cubic feet.
[ ] [ ] [ ] Excavated side slopes should be 2:1.
[ ] [ ] [ ] 2” x 4” frame is constructed and structurally sound.
[ ] [ ] [ ] Posts 3-foot maximum spacing between posts.
[ ] [ ] [ ] Fabric is embedded 1 to 1.5 feet below ground and secured to frame/posts with staples at max 8-
inch spacing.
[ ] [ ] [ ] Posts are stable, fabric is tight and without rips or frayed areas.
[ ] [ ] [ ] Manufactured insert fabric is free of tears and punctures.
[ ] [ ] [ ] Filter Sock is not torn or flattened and fill material is contained within the mesh sock.
[ ] [ ] [ ] Outlet structure is constructed per the approved plan or drawing.
[ ] [ ] [ ] Geotextile fabric has been placed beneath rock fill.
[ ] [ ] [ ] Sediment trap slopes and disturbed areas are stabilized.
[ ] [ ] [ ] Basin and outlet structure constructed per the approved plan.
[ ] [ ] [ ] Basin side slopes are stabilized with seed/mulch.
[ ] [ ] [ ] Drainage structure flushed and basin surface restored upon removal of sediment basin facility.
[ ] [ ] [ ] Sediment basin dewatering pool is dewatering at appropriate rate.
Note:
Not all erosion and sediment control practices are included in this listing. Add additional pages
to this list as required by site specific design. All practices shall be maintained in accordance
with their respective standards.
Construction inspection checklists for post-development stormwater management practices can
be found in Appendix F of the New York Stormwater Management Design Manual.
b. Modifications to the SWPPP (To be completed as described below)
1. There is a significant change in design, construction, operation, or maintenance which may have a
significant effect on the potential for the discharge of pollutants to the waters of the United States and which
has not otherwise been addressed in the SWPPP; or
2. The SWPPP proves to be ineffective in:
a. Eliminating or significantly minimizing pollutants from sources identified in the SWPPP and as required
by this permit; or
b. Achieving the general objectives of controlling pollutants in stormwater discharges from permitted
construction activity; and
3. Additionally, the SWPPP shall be amended to identify any new contractor or subcontractor that will
implement any measure of the SWPPP.
b.
"I certify under penalty of law that this document and all attachments were prepared under my
direction or supervision in accordance with a system designed to assure that qualified personnel
properly gathered and evaluated the information submitted. Based on my inquiry of the person or
persons who manage the system, or those persons directly responsible for gathering the information,
the information submitted is, to the best of my knowledge and belief, true, accurate, and complete.
Further, I hereby certify that the SWPPP meets all Federal, State, and local erosion and sediment
control requirements. I am aware that false statements made herein are punishable as a class A
misdemeanor pursuant to Section 210.45 of the Penal Law. "
Title
Date:
Phone:
Email:
“ I hereby certify that I meet the criteria set forth in the General Permit to conduct site inspections for
this project and that the appropriate erosion and sediment controls described in the SWPPP and as
described in the following Pre-construction Site Assessment Checklist have been adequately installed
or implemented, ensuring the overall preparedness of this site for the commencement of
construction.”
Title
Date:
Phone:
Email:
“I hereby certify that I understand and agree to comply with the terms and conditions of the SWPPP
and agree to implement any corrective actions identified by the qualified inspector during a site
inspection. I also understand that the owner or operator must comply with the terms and conditions of
the most current version of the New York State Pollutant Discharge Elimination System (“SPDES”)
general permit for stormwater discharges from construction activities and that it is unlawful for any
person to cause or contribute to a violation of water quality standards. Furthermore, I understand that
certifying false, incorrect or inaccurate information is a violation of the referenced permit and the
laws of the State of New York and could subject me to criminal, civil and/or administrative
proceedings.”
Date
Print Name
Title
Signature of Trained Contractor
Date
Print Name of Trained Contractor
Title
Name of Contracting Firm
Street Address
City, State, Zip
Telephone No.
A copy of this statement shall be retained as part of the Stormwater Pollution Prevention Plan (SWPPP) for a period
off at least five (5) years after the subject property is stabilized.
TAHESHA L. WAY
Lt. Governor
SHAWN M. LATOURETTE
Commissioner
DEPARTMENT OF ENVIRONMENTAL PROTECTION
DIVISION OF WATERSHED PROTECTION AND RESTORATION
BUREAU OF NJPDES STORMWATER PERMITTING & WATER QUALITY MANAGEMENT
P.O. Box 420 Mail Code 501-02A
Trenton, New Jersey 08625-0420
609-633-7021 / Fax: 609-777-0432
https://dep.nj.gov/stormwater/
October 3, 2024
Jeremy Fink, P.E.
Associate Director of Product Development
Hydro International
94 Hutchins Drive
Portland, ME 04102
Re:
Hydro-Shield Advance Plus Hydrodynamic Separator
Online Installation
TSS Removal Rate 50%
Dear Mr. Fink:
The Stormwater Management rules under N.J.A.C. 7:8-5.2(f) and 5.2(j) allow the use of manufactured
treatment devices (MTDs) for compliance with the design and performance standards at N.J.A.C. 7:8-5 if
the pollutant removal rates have been verified by the New Jersey Corporation for Advanced Technology
(NJCAT) and have been certified by the New Jersey Department of Environmental Protection (NJDEP).
Hydro International has requested a Laboratory Certification for the Hydro-Shield Advance Plus
Hydrodynamic Separator (Hydro-Shield Advance Plus).
The project falls under the “Procedure for Obtaining Verification of a Stormwater Manufactured Treatment
Device from New Jersey Corporation for Advance Technology” dated August 4, 2021. The applicable
protocol is the “New Jersey Laboratory Testing Protocol to Assess Total Suspended Solids Removal by a
Hydrodynamic Sedimentation Manufactured Treatment Device” dated January 1, 2021, and last updated
April 25, 2023.
NJCAT verification documents submitted to the NJDEP indicate that the requirements of the
aforementioned protocol have been met or exceeded. The NJCAT letter also included a recommended
certification TSS removal rate and the required maintenance plan. The NJCAT Verification Report with
the Verification Appendix (dated September 2024) for this device is published online at
http://www.njcat.org/verification-process/technology-verification-database.html.
The NJDEP certifies the use of the Hydro-Shield Advance Plus by Hydro International at a TSS
removal rate of 50% when designed, operated and maintained in accordance with the information
provided in the Verification Appendix and the following conditions:
New Jersey is an Equal Opportunity Employer l Printed on Recycled Paper and Recyclable
1. The maximum treatment flow rate (MTFR) for the manufactured treatment device (MTD) is
calculated using the New Jersey Water Quality Design Storm (1.25 inches in 2 hrs) in N.J.A.C. 7:8-
5.5.
2. The Hydro-Shield Advance Plus stormwater treatment device shall be installed using the same
configuration reviewed by NJCAT and shall be sized in accordance with the criteria specified in
item 6 below.
3. This Hydro-Shield Advance Plus stormwater treatment device cannot be used in series with another
MTD or a media filter (such as a sand filter) to achieve an enhanced removal rate for total suspended
solids (TSS) removal under N.J.A.C. 7:8-5.5.
4. Additional design criteria for MTDs can be found in Chapter 11.3 of the New Jersey Stormwater
Best Management Practices (NJ Stormwater BMP) Manual which can be found on-line at
https://dep.nj.gov/stormwater/.
5. The maintenance plan for a site using this device shall incorporate, at a minimum, the maintenance
requirements for the Hydro-Shield Advance Plus. A copy of the maintenance plan is attached to
this certification. However, it is recommended to review the maintenance website at https://hydro-
int.com/sites/default/files/2024-09/HSA_OandM_.pdf for any changes to the maintenance
requirements.
The example below demonstrates the sizing procedure for the Hydro-Shield Advance Plus:
A 0.25-acre impervious site with a slope of 5% is to be treated to 50% TSS removal
using a Hydro-Shield Advance Plus. The hydraulically most distant point to the inlet
of the Hydro-Shield Advance Plus is 110 feet. The site is located in an area for which
the projected 2-year storm rainfall depth was calculated to be 3.84 inches.
The site runoff (Q) was based on the following:
CN = 98 (Curve Number for impervious)
Dimensionless Unit Hydrograph (DUH) = SCS Standard DUH (peak rate factor of 484)
Time of concentration = 0.8 minutes
Q = 0.77 cfs
Given the site runoff is 0.77 cfs and based on Table 1 below, the Hydro-Shield Advance Plus 4-ft
Model with an MTFR of 1.49 cfs would be the smallest model approved that could be used for this
site that could remove 50% of the TSS from the impervious area without exceeding the MTFR.
The sizing table corresponding to the available system models is noted below. Additional
specifications regarding each model can be found in the Verification Appendix.
Table 1: Hydro-Shield Advance Plus Models and Associated MTFRs
Hydro-Shield
Advance Plus
Model
Diameter
(ft)
Maximum
Treatment
Flow Rate
(cfs)
Effective
Treatment
Area
(sq. ft.)
Hydraulic
Loading Rate
(gpm/sq. ft.)
4-ft
1.49
12.6
53.1
6-ft
3.35
28.3
53.1
8-ft
5.95
50.3
53.1
Be advised a detailed maintenance plan is mandatory for any project with a Stormwater BMP subject to the
Stormwater Management Rules, N.J.A.C. 7:8. The plan must include all the items identified in the
Stormwater Management Rules, N.J.A.C. 7:8-5.8. Such items include, but are not limited to, the list of
inspection and maintenance equipment and tools, specific corrective and preventative maintenance tasks,
indication of problems in the system, and training of maintenance personnel. Additional information can
be found in Chapter 8: Maintenance and Retrofit of Stormwater Management Measures.
If you have any questions regarding the above information, please contact Lisa Schaefer of my office at
lisa.schaefer@dep.nj.gov.
Bureau of NJPDES Stormwater Permitting & Water Quality Management
Division of Watershed Protection and Restoration
New Jersey Department of Environmental Protection
Attachment: Maintenance Plan
c:
Hydro-Shield™ Advance
Hydrodynamic Separator for Stormwater Treatment
Table of Contents
Hydro-ShieldTM Advance by Hydro International
- Introduction
- Operation
- Pollutant Capture and Retention
Model Sizes and Configuration
- Hydro-ShieldTM Advance Components
Maintenance
- Overview
- Maintenance Equipment Considerations
- Determining Your Maintenance Schedule
Maintenance Procedures
- Inspection
- Floatables and Sediment Clean Out
Hydro-ShieldTM Advance Installation Log
Hydro-ShieldTM Advance Inspection and Maintenance Log
COPYRIGHT STATEMENT: The contents of this manual, including the graphics contained herein, are intended for the use of the recipient to whom the document
and all associated information are directed. Hydro International plc owns the copyright of this document, which is supplied in confidence. It must not be used for any
purpose other than that for which it is supplied and must not be reproduced, in whole or in part stored in a retrieval system or transmitted in any form or by any
means without prior permission in writing from Hydro International plc. Hydro-Shield™ Advance is a trademarked hydrodynamic vortex separation device of Hydro
International plc. A patent covering the Hydro-Shield™ Advance has been granted.
DISCLAIMER: Information and data contained in this manual is exclusively for the purpose of assisting in the operation and maintenance of Hydro International
plc’s First Defense®. No warranty is given nor can liability be accepted for use of this information for any other purpose. Hydro International plc has a policy of
continuous product development and reserves the right to amend specifications without notice.
I. Hydro-Shield™ Advance by Hydro International
Introduction
The Hydro-Shield™ Advance leads a new generation of hydrodynamic separator for stormwater treatment that utilize lamella technology for
optimal settling performance. It efficiently removes total suspended solids (TSS), trash and hydrocarbons from stormwater runoff without washing
out previously captured pollutants while providing an internal peak flow bypass. The Hydro-Shield™ Advance is available in multiple model
configurations to accommodate a wide range of pipe sizes, peak flows and depth constraints.
The Hydro-Shield™ Advance operates on simple fluid hydraulics combined with a lamella treatment module for increased efficiency. It is self-
activating, has no moving parts, no external power requirement and is fabricated with durable non-corrosive components. No manual procedures
are required to operate the unit and maintenance is limited to monitoring accumulations of stored pollutants and periodic clean-outs. The Hydro-
Shield™ Advance has been designed to allow for easy and safe access for inspection, monitoring and clean-out procedures. Neither entry into
the unit nor removal of the internal components is necessary for maintenance, thus safety concerns related to confined-space-entry are avoided.
The internal components of the Hydro-Shield™ Advance have been designed to optimize pollutant capture. Sediment is captured and retained in
the base of the unit (Fig.1).
The pollutant storage volumes are isolated from the built-in bypass chamber to prevent washout during high-flow storm events. The sump of the
Hydro-Shield™ Advance retains a standing water level between storm events. This ensures a quiescent flow regime at the onset of a storm,
preventing resuspension and washout of pollutants captured during previous events.
•
Stormwater treatment at the point of entry into the drainage line
•
Sites constrained by space, topography or drainage profiles with limited slope and depth of cover
•
Retrofit installations where stormwater treatment is placed on or tied into an existing storm drain line
•
Pretreatment for filters, infiltration and storage
Advantages
•
Integral bypass conveys large peak flows without the need for “offline” arrangements using separate junction manholes
•
Advanced Treatment module for effective sediment capture
•
Easy installation and maintenance
•
Accommodates large pipe diameters
Figure 1: Pollutant storage volume in the Hydro-Shield™ Advance
Sediment
Storage
II. Model Sizes & Configurations
The Hydro-Shield™ Advance inlet and internal bypass arrangements are available in several model sizes and configurations.
All Hydro-Shield™ Advance models include the internal components that are designed to remove and retain total suspended solids (TSS), (Fig.2).
Hydro-Shield™ Advance model sizes (diameter) are shown in Table 1.
Hydro-Shield™ Advance Components
1.
Inlet Pipe
2.
Treatment Module
3.
Outlet Module
4.
Outlet Pipe
5.
Internal Bypass
6.
Sediment Storage
7.
Cover(s)
Hydro-Shield Advance
Model Sizes (MH Dia.)
HSA-4ft
HSA-6ft
HSA-8ft
Overview
The Hydro-Shield™ Advance protects the environment by removing a wide range of pollutants from stormwater runoff. Periodic removal of these
captured pollutants is essential to the continuous, long-term functioning of the Hydro-Shield™ Advance. The unit will efficiently capture and
retain sediment until the stated sediment storage capacity has been reached. The Hydro-Shield™ Advance will continue to operate afterwards
but prolonged operation will reduce removal efficiency and may cause damage to the equipment.
The Hydro-Shield™ Advance allows for easy and safe inspection, monitoring and clean-out procedures. A commercially or municipally owned
sump-vac is used to remove the captured sediment. Access ports are located in the top of the manhole. Maintenance events may include
inspection, floatables removal, or sediment removal. Maintenance events do not require entry into the manhole, nor do they require the internal
components of the Hydro-Shield™ Advance to be removed. In the case of inspection and floatables removal, a vactor truck is not required.
However, a vactor truck is required if the maintenance event is to include sediment removal.
The internal components of the Hydro-Shield™ Advance have a dedicated area on the perimeter through which the sediment storage sump can
be accessed with a sump vac hose. Access to the Outlet Module is also provided. (Fig.3). On 4ft units, access is via a shared manhole cover.
Larger units are provided with 2 separate covers.
The frequency of clean-out is determined in the field after installation. During the first year of operation, the unit should be inspected every six
months to determine the rate of sediment and floatables accumulation. A simple probe such as a Sludge-Judge® can be used to determine the
level of accumulated solids stored in the sump. This information can be recorded in the maintenance log (see page 9) to establish a routine
maintenance schedule.
The vactor procedure, including both sediment and floatables removal, for Hydro-Shield™ Advance typically takes less than 30 minutes
Fig.3 Hydro-Shield™ Advance maintenance access.
Sediment Cleanout Access
Outlet Module Access
Inspection Procedures
1. Set up any necessary safety equipment around the access
port or grate of the Hydro-Shield™ Advance as stipulated by
local ordinances. Safety equipment should notify passing
pedestrian and road traffic that work is being done.
2. Remove the manhole lid(s).
3. Without entering the vessel, look down into the chamber to
inspect the inside. Make note of any irregularities. Fig.4
shows the standing water level that should be observed.
4. Without entering the vessel, use the pole with the skimmer net
to remove floatables and loose debris from the components
and water surface.
5. Using a sediment probe such as a Sludge Judge®, measure
the depth of sediment that has collected in the sump of the
vessel.
6. On the Maintenance Log (see page 9), record the date, unit
location, estimated volume of floatables and gross debris
removed, and the depth of sediment measured. Also note
any apparent irregularities such as damaged components or
blockages.
7. Securely replace the grate or lid.
8. Take down safety equipment.
9. Notify Hydro International of any irregularities noted during
inspection
Floatables and Sediment Clean Out
Floatables clean out is typically done in conjunction with sediment
removal.
A commercially or municipally owned sump-vac is used to remove
captured sediment
and floatables (Fig.4).
Floatables and loose debris can also be netted with a skimmer
and pole.
The access port located at the top of the manhole provides
unobstructed access
for a vactor hose to be lowered to the base of the sump.
• Floatables and sump clean out are typically conducted once
a year during any season.
• Floatables and sump clean out should occur as soon as
possible following a spill in the contributing drainage area.
• Safety Equipment (traffic cones, etc)
• Crow bar or other tool to remove grate or lid
• Pole with skimmer or net (if only floatables are being removed)
• Sediment probe (such as a Sludge Judge®)
• Vactor truck (flexible hose recommended)
-
Spray hose or wand and clean water
• Hydro-Shield™ Advance Maintenance Log
Fig.4 Floatables are removed with a vactor hose
Hydro International, 94 Hutchins Drive, Portland ME04102
Tel: +1 (207) 756 6200 Fax: +1 (207) 756 6212 Web: hydro-int.com
Procedures Floatables and Sediment Clean Out Procedures
1. Set up any necessary safety equipment around the access
port or grate of the Hydro-Shield™ Advance as stipulated by
local ordinances. Safety equipment should notify passing
pedestrian and road traffic that work is being done.
2. Remove the lid(s) to the manhole.
3. Without entering the vessel, look down into the chamber to
inspect the inside. Make note of any irregularities.
4. Remove floatables on the surface of the water
with the vactor hose or with the skimmer or net
5. Using a sediment probe such as a Sludge Judge®, measure
the depth of sediment that has collected in the sump of the
vessel and record it in the Maintenance Log (page 9).
6. Once all floatables have been removed, drop the vactor hose
to the base of the sump. Vactor out the sediment and gross
debris off the sump floor
7. Once the water level is below the Treatment Module, visually inspect the Outlet Module and inside of the Treatment Module
8. If necessary, use a spray hose or wand to dislodge any debris or silt and flush them into the sump.
9. Retract the vactor hose from the vessel.
10. On the Maintenance Log provided by Hydro International,
record the date, unit location, estimated volume of floatables
and gross debris removed, and the depth of sediment
measured. Also note any apparent irregularities such as
damaged components, blockages, or irregularly high or low
water levels.
11. Securely replace the lid(s).
- Every 6 months after the first year of installation
- Once per year, with sediment removal
- Following a spill in the drainage area
- Once per year or as needed
- Following a spill in the drainage area
Inspection
Floatables Removal
Sediment Removal
Activity Frequency
NOTE: For most clean outs the entire volume of liquid does not need to be removed from the manhole. Only remove the first few
inches of oils and floatables from the water surface to reduce the total volume of liquid removed during a clean out
Hydro-Shield™ Advance Installation Log
HYDRO INTERNATIONAL REFERENCE NUMBER:
OWNER:
FAX:
FAX:
INSTALLATION DATE:
/
/
MODEL SIZE (CIRCLE ONE):
INLET :
Hydro-Shield™ Advance Inspection and Maintenance Log
Date
Initials
Depth of
Floatables
and Oils
Sediment
Depth
Measured
Volume of
Sediment
Removed
Site Activity and
Comments
Hydro-Shield
TM Advance
The Hydro-Shield™ Advance is a next
generation hydrodynamic separator designed
for optimal stormwater treatment, utilizing
lamella technology to remove pollutants. With
flexible design options it effectively prevents
pollutant washout during high-flow storm
events, ensuring reliable performance under
varying conditions.
Highest Flow Rates on the Market
Flexible Configurations
Ease of Maintenance
Advanced Hydrodynamic Separation
Advanced
Hydrodynamic
Separation
Leveraging over 40 years of engineering excellence, the Hydro-ShieldTM Advance was designed by the leading
water experts from Hydro International, developers of Downstream Defender® and First Defense®. With
NJCAT2021 protocol approval, utilize the advanced hydrodynamic separator with the highest treatment flow
rate available on the market.
• Removal of total suspended solids (TSS) and floatable trash from
stormwater runoff
• New construction or redevelopment of commercial and residential sites
• Pollutant hotspots such as maintenance yards, parking lots, gas stations,
streets, highways, airports and transportation hubs
• Site constrained LID or green infrastructure-based developments
• LEED® development projects
1. Governed by peak hydraulic flow of max pipe size.
2. If exceeded, system will enter bypass at lower flow rates than the
stated MTF.
3. Current NJ approval for a single inlet pipe, co-linear with outlet pipe
(no inlet pipe angle).
4. Recommended maintenance intervals, based on 50% full sump:
Shallow 154 months
Standard 70 months
Plus 45 months
Technical Specifications
Hydro-ShieldTM Advance - Sizing Table
Unit
Size
Configuration
Model
Number
Max WQ
Flow [cfs]
Peak Flow1
[cfs]
Max Pipe
Size [in]
4 FT
Shallow
HSA-4S
0.44
7.4
Standard
HSA-4
0.96
7.4
Plus
HSA-4P
1.48
7.4
6 FT
Shallow
HSA-6S
0.98
Standard
HSA-6
2.16
Plus
HSA-6P
3.33
Power Flow, High Removal Efficiency.
Revision 12/2024
4-A-111
Trusted partnerships.
Full scale solutions.
www.oldcastleinfrastructure.com | (888) 965-3227
Feature
Benefit
Highest treatment flow rate available on the market.
Smaller Footprint for lower costs.
Bypass flow only limited by pipe size.
Easy retrofit design and online use to reduce number
of structures and manage cost.
Configurable cone stacks by manhole size and depth.
More flexible depth and footprint configurations when working in space con-
strained sites, especially rock or high ground water.
Model size overlap.
Pipe size, peak flows, and treatment flows are not locked to one size chamber,
allowing for optimized design and cost control.
Treatment flow overlap.
Engineers don't have to specify the exact model, allowing contractors to work
with us based on site conditions and other factors to get the best value option.
APPENDIX G
Pipe Sizing Calculations
Design Storm:
25-Year
FROM
TO
A (ac.)
C
CA
A (ac.)
C
CA
INLET
PIPE
TOTAL
DESIGN CAP.
V(ft/s)
n
s (%)
L (ft)
DIA (in)
FROM
TO
CB 3C
CB 3B
0.15
0.9
0.14
0.00
0.3
0.00
0.14
-
7.2
1.0
4.2
4.4
0.012
1.2
CB 3C
CB 3B
CB 3B
CB 3A
0.05
0.9
0.05
0.00
0.3
0.00
0.19
-
7.2
1.4
5.2
5.6
0.012
1.8
CB 3B
CB 3A
CB 3A
CB 3
0.09
0.9
0.08
0.02
0.3
0.01
0.28
-
7.2
2.0
6.0
6.9
0.012
2.4
CB 3A
CB 3
CB 3
CB 2
0.05
0.9
0.05
0.02
0.3
0.01
0.34
-
7.2
2.4
6.6
7.8
0.012
2.9
CB 3
CB 2
CB 2
HDS 1.1
0.47
0.9
0.42
0.06
0.3
0.02
0.78
-
7.2
5.6
11.9
9.6
0.012
2.9
CB 2
HDS 1.1
HDS 1.1
EX DI
0.00
0.9
0.00
0.00
0.3
0.00
0.78
-
7.2
5.6
24.1
11.2
0.012
4.5
HDS 1.1
EX DI
CB 8
CB 7
0.10
0.9
0.09
0.00
0.3
0.00
0.09
-
7.2
0.6
5.5
4.7
0.012
2.0
CB 8
CB 7
CB 7
DMH 6
0.10
0.9
0.09
0.00
0.3
0.00
0.18
-
7.2
1.3
3.0
3.7
0.012
0.6
CB 7
DMH 6
DMH 6
HDS 2.1
0.00
0.9
0.00
0.00
0.3
0.00
0.33
-
7.2
2.4
4.9
4.0
0.012
0.5
DMH 6
HDS 2.1
HDS 2.1
DI 5
0.00
0.9
0.00
0.00
0.3
0.00
0.33
-
7.2
2.4
7.3
5.4
0.012
1.1
HDS 2.1
DI 5
DI 5
DI 4
0.15
0.9
0.14
0.00
0.3
0.00
0.69
-
7.2
5.0
7.7
6.7
0.012
1.2
DI 5
DI 4
CB 6B
CB 6A
0.05
0.9
0.05
0.00
0.3
0.00
0.05
-
7.2
0.4
3.0
2.6
0.012
0.6
CB 6B
CB 6A
CB 6A
DMH 6
0.05
0.9
0.05
0.00
0.3
0.00
0.10
-
7.2
0.7
3.7
3.6
0.012
0.9
CB 6A
DMH 6
CB 6C
DMH 6
0.05
0.9
0.05
0.00
0.3
0.00
0.05
-
7.2
0.4
3.7
3.0
0.012
0.9
CB 6C
DMH 6
DI 5A
DI 5
0.05
0.9
0.05
0.57
0.3
0.17
0.22
-
7.2
1.6
3.0
3.9
0.012
0.6
DI 5A
DI 5
STRUCTURE
STRUCTURE
IMPERVIOUS AREA
PERVIOUS AREA
TIME OF CONC. (min.)
JOB NUMBER: 24154.100
I
CA
DATE: 4-30-2025
PROJECT: Croton Point
DRAINAGE SYSTEM CALCULATIONS
CHK: JWM
PIPE DESIGN
DATE: 4-30-2025
BY: CMS
Q (cfs)
Y:\Insite Forms\Design\Stormwater\Pipe Sizing\Pipe Sizing Calc.xls
1 Croton Point — SWPPP
SWPPP24154.doc
Insite Engineering, Surveying & Landscape Architecture, P.C.
APPENDIX H
OPRHP/SHPO Determination Letter
KATHY HOCHUL
Governor
RANDY SIMONS
Commissioner Pro Tempore
September 03, 2024
Jan Johannessen, RLA, AICP
Principal
KSCJ Consulting
500 Main Street
Armonk, NY 10504
Re: SEQRA
1 Croton Point
1 Croton Point Ave, Croton On Hudson, NY 10520
24PR07889
Dear Jan Johannessen, RLA, AICP:
Thank you for requesting the comments of the Office of Parks, Recreation and Historic
Preservation (OPRHP). We have reviewed the project in accordance with the New York State
Historic Preservation Act of 1980 (Section 14.09 of the New York Parks, Recreation and Historic
Preservation Law). These comments are those of the OPRHP and relate only to Historic/Cultural
resources. They do not include potential environmental impacts to New York State Parkland that
may be involved in or near your project.
Based upon this review, it is the opinion of OPRHP that no properties, including archaeological
and/or historic resources, listed in or eligible for the New York State and National Registers of
Historic Places will be impacted by this project.
If further correspondence is required regarding this project, please be sure to refer to the
OPRHP Project Review (PR) number noted above. If you have any questions, please contact
Chelsea Towers at the following email address:
Chelsea.Towers@parks.ny.gov
Sincerely,
R. Daniel Mackay
Deputy Commissioner for Historic Preservation
Division for Historic Preservation
New York State Office of Parks, Recreation and Historic Preservation
Division for Historic Preservation, Peebles Island, PO Box 189, Waterford, New York 12188-0189
(518) 237-8643 • https://parks.ny.gov/shpo
1 Croton Point — SWPPP
SWPPP24154.doc
Insite Engineering, Surveying & Landscape Architecture, P.C.
FIGURES
LANDSCAPE ARCHITECTURE, P.C.
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ENGINEERING, SURVEYING &
LANDSCAPE ARCHITECTURE, P.C.
Z:\E\24154100 WBP Croton Point Ave\Stormwater\Figures\Figure 2 - Pre Development Map.dwg, 4/28/2025 6:35:14 PM, jmcmanus, 1:1
ENGINEERING, SURVEYING &
LANDSCAPE ARCHITECTURE, P.C.
·
·
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Machine-extracted for search and reference — the original PDF is the authoritative version.