A. 
For all regulated activities, unless preparation of an SWM Site Plan is specifically exempted in § 294-14:
(1) 
Preparation and implementation of an approved SWM Site Plan is required.
(2) 
No regulated activities shall commence until:
(a) 
The Municipality issues written approval of an SWM Site Plan, which demonstrates compliance with the requirements of this chapter; and
(b) 
The Applicant has received a letter of adequacy or approval for the Erosion and Sediment Control Plan review by the Municipality and the Conservation District (if required), and has received all other local, State and Federal permit approvals required for the project involving the Regulated Activity.
B. 
Neither submission of an SWM Site Plan under the provisions herein nor compliance with the provisions of this chapter shall relieve any person from responsibility for damage to any person or property otherwise imposed by law.
C. 
SWM Site Plans approved by the Municipality, in accordance with § 294-30, shall be on site throughout the duration of the regulated activity.
D. 
The Municipality may, after consultation with DEP, approve measures for meeting the state water quality requirements other than those in this chapter, provided that such alternative measures meet the minimum requirements of, and do not conflict with, state law including, but not limited to, the Clean Streams Law.
E. 
For all regulated earth disturbance activities, erosion and sediment control BMPs shall be designed, implemented, operated, and maintained during the regulated earth disturbance activities (e.g., during construction) to meet the purposes and requirements of this chapter and to meet all requirements under Title 25 of the Pennsylvania Code and the Clean Streams Law. Various BMPs and their design standards are listed in the Erosion and Sediment Pollution Control Program Manual (E&S Manual3), No. 363-2134-008, as amended and updated.
F. 
Impervious areas:
(1) 
The measurement of impervious areas shall include all of the impervious areas in the total proposed development even if development is to take place in stages.
(2) 
For development taking place in stages, the entire development plan shall be used in determining compliance with this chapter.
(3) 
For projects that add impervious area to a parcel, the total impervious area on the parcel is subject to the requirements of this chapter; except that the volume controls in § 294-15 and the peak rate controls of § 294-18 do not need to be retrofitted for existing impervious areas that are not being altered by the proposed regulated activity.
G. 
Stormwater flows onto adjacent property shall not be created, increased, relocated, or otherwise altered without written notification to the adjacent property owner(s). Such stormwater flows shall be subject to the requirements of this chapter.
H. 
All regulated activities shall include such measures as necessary to:
(1) 
Protect health, safety, and property.
(2) 
Meet the water quality goals of this chapter by implementing measures to:
(a) 
Minimize disturbance to floodplains, wetlands, and wooded areas.
(b) 
Maintain or extend riparian buffers.
(c) 
Avoid erosive flow conditions in natural flow pathways.
(d) 
Minimize thermal impacts to waters of this Commonwealth.
(e) 
Disconnect impervious surfaces by directing runoff to pervious areas, wherever possible.
(3) 
Incorporate methods described in the Pennsylvania Stormwater Best Management Practices Manual (PA BMP Manual). If methods other than green infrastructure and LID methods are proposed to achieve the volume and rate controls required under this chapter, the SWM Site Plan must include a detailed justification demonstrating that the use of LID and green infrastructure is not practicable.
I. 
For areas underlain by Karst or carbonate geology that may be susceptible to the formation of sinkholes and other Karst features, the location, type, and design of infiltration BMPs shall be based on a Site evaluation conducted by a qualified Licensed Professional and based on the PA BMP Manual (as amended) or other design guidance acceptable to the Municipal Engineer.
J. 
Infiltration BMPs should be spread out, made as shallow as practicable, and located to maximize use of natural on-site infiltration features while still meeting the other requirements of this chapter.
K. 
Normally dry, open top, storage facilities should completely drain both the volume control and rate control capacities over a period of time not less than 24 and not more than 72 hours from the end of the design storm.
L. 
The design of all BMPs and Conveyances shall incorporate sound engineering principles and practices in a manner that does not aggravate existing stormwater problems as identified by the Municipality. The Municipality reserves the right to disapprove any design that would result in construction in an area affected by existing stormwater problem(s) or continuation of an existing stormwater problem(s).
M. 
The design storm volumes to be used in the analysis of peak rates of discharge should be obtained from the latest version of the Precipitation-Frequency Atlas of the United States, National Oceanic and Atmospheric Administration (NOAA), National Weather Service, Hydrometeorological Design Studies Center, Silver Spring, Maryland. NOAA's Atlas 14 can be accessed at: http://hdsc.nws.noaa.gov/hdsc/pfds/.
N. 
For all regulated activities, SWM BMPs shall be designed, implemented, operated, and maintained to meet the purposes and requirements of this chapter and to meet all requirements under Title 25 of the Pennsylvania Code, the Clean Streams Law, and the Storm Water Management Act.
O. 
Various BMPs and their design standards are listed in the BMP Manual.
P. 
Areas located outside of the Site (i.e., areas outside of the Regulated Activity) that drain through a proposed Site are not subject to water quality and volume control, infiltration, stream channel protection, or peak flow rate control requirements (as presented in §§ 294-15, 294-16, 294-17, and 294-18). Drainage facilities located on the Site shall be designed to safely convey flows from outside of the Site through the Site.
Q. 
Existing wetlands, either on the Site or on an adjacent property, shall not be used to meet the minimum design requirements for stormwater management or stormwater runoff quality treatment. Stormwater discharges to existing wetlands shall not degrade the quality or hydrologic integrity of the wetland.
R. 
Hotspots runoff controls. Specific structural or pollution prevention practices may be required, as determined to be necessary by the Municipal Engineer, to pretreat runoff from Hotspots prior to infiltration. Following is a list of examples of Hotspots:
(1) 
Vehicle salvage yards and recycling facilities;
(2) 
Vehicle fueling stations;
(3) 
Vehicle service and maintenance facilities;
(4) 
Vehicle and equipment cleaning facilities;
(5) 
Fleet storage areas (bus, truck, etc.);
(6) 
Industrial sites based on Standard Industrial Classification Codes;
(7) 
Marinas (service and maintenance areas);
(8) 
Outdoor liquid container storage;
(9) 
Outdoor loading/unloading facilities;
(10) 
Public works storage areas;
(11) 
Facilities that generate or store hazardous materials;
(12) 
Commercial container nursery;
(13) 
Contaminated sites/brownfields;
(14) 
Other land uses and activities as designated by the Municipality.
S. 
Additional water quality requirements. The Municipality may require additional stormwater control measures for stormwater discharges to special management areas including, but not limited to:
(1) 
Water bodies listed as "impaired" by PADEP.
(2) 
Any water body or watershed with an approved Total Maximum Daily Load (TMDL).
(3) 
Areas of known existing flooding problems.
(4) 
Critical areas with sensitive resources (e.g., State designated special protection waters, cold water fisheries, carbonate geology or other groundwater recharge areas that may be highly vulnerable to contamination, drainage areas to water supply reservoirs, etc.).
T. 
All Regulated Activities located within a Special Flood Hazard Area designated by the Federal Emergency Management Agency (FEMA) shall comply with Chapter 117 of the Marietta Borough Code of Ordinances, more specifically known as the "Marietta Borough Floodplain Management Ordinance" and shall be designed to maintain the flood carrying capacity of the floodway such that the base flood elevations are not increased, either upstream or downstream. The natural conveyance characteristics of the Site and the receiving floodplain shall be incorporated into the stormwater management practices proposed for the Site.
A. 
General exemptions. Regulated activities that involve less than or equal to 240 square feet of proposed impervious surfaces and less than or equal to 5,000 square feet of earth disturbance or are listed in Subsection H are exempt from those (and only those) requirements of this chapter that are included in the sections and articles listed in Table 302.1. Exemptions are for the items noted in Table 302.1 only and shall not relieve the landowner from other applicable requirements of this chapter. Exemption shall not relieve the Applicant from implementing such measures as are necessary to protect health, safety, and welfare, property, and water quality.
B. 
Agricultural activity is exempt from the SWM Site Plan preparation requirements of this chapter provided the activities are performed according to the requirements of 25 Pa. Code Chapter 102.
C. 
Forest management and timber operations are exempt from the SWM Site Plan preparation requirements of this chapter provided the activities are performed according to the requirements of 25 Pa. Code Chapter 102.
D. 
Exemptions from any provisions of this chapter shall not relieve the Applicant from the requirements in § 294-13E through M.
E. 
The Municipality may deny or revoke any exemption or modified requirements pursuant to this section at any time for any project that the Municipality believes may pose a threat to public health and safety or the environment.
F. 
Requirements for exempt activities.
(1) 
An exemption from any requirement of this chapter shall not relieve the Applicant from implementing all other applicable requirements of this chapter or from implementing such measures as are necessary to protect public health, safety, and welfare, property and water quality.
(2) 
An exemption shall not relieve the Applicant from complying with the requirements for State-designated special protection waters designated by PADEP as high quality (HQ) or exceptional value (EV) waters, or any other current or future State or municipal water quality protection requirements.
(3) 
An exemption under this chapter shall not relieve the Applicant from complying with all other applicable municipal ordinances or regulations.
(4) 
Any Applicant desiring exemption from design, plan submission, and plan processing requirements shall complete an application for exemption in the form available at the Muncipality's office and pay any applicable filing fee.
Table 302.1
Thresholds for Regulated Activities Exempt from Chapter Provisions
Ordinance Article/Section
Activities Listed In § 294-14A
< 240 Square Feet of Proposed Impervious Surfaces AND < 5,000 Square Feet of Proposed Earth Disturbance
> 240 Square Feet of Proposed Impervious Surfaces OR > 5,000 Square Feet of Proposed Earth Disturbance
Article I
Not exempt
Not exempt
Not exempt
Article II
Not exempt
Not exempt
Not exempt
§§ 294-22 and 294-13E
Not exempt
Not exempt
Not exempt
§§ 294-13, 294-15, 294-16, 294-17, 294-18, 294-19, and 294-20
Exempt
Exempt
Not exempt
Article IV
Exempt
Exempt
Not exempt
Article V
Exempt
Exempt
Not exempt
Article VI
Exempt
Exempt
Not exempt
Article VII
Not exempt
Not exempt
Not exempt
Article VIII
Not exempt
Not exempt
Not exempt
Other Erosion, Sediment and Pollution Control Requirements
Must comply with Title 25, Chapter 102 of the PA Code and other applicable State and municipal codes, including the Clean Streams Law.
G. 
Exemptions for specific activities. The following specific Regulated Activities are exempt from the requirements of §§ 294-13, 294-15, 294-16, 294-17, 294-18, 294-19, and 294-20, and Article IV, Article V, and Article VI of this chapter (as shown in Table 302.1), unless otherwise noted below. All other conveyance and system design standards established by the Municipality in other codes or ordinances shall be required, and all other provisions of this chapter shall apply.
(1) 
Emergency exemption. Emergency maintenance work performed for the protection of public health, safety and welfare. This exemption is limited to repair of an existing Stormwater Management Facility; upgrades, additions or other improvements are not exempt. A written description of the scope and extent of any emergency work performed shall be submitted to the Municipality within two business days of the commencement of the activity. A detailed plan shall be submitted no later than 30 calendar days following commencement of the activity. If the Municipality finds that the work is not an emergency, then the work shall cease immediately and the requirements of this chapter shall be addressed as applicable.
(2) 
Maintenance. Any maintenance to an existing Stormwater Management Facility, BMP or Conveyance made in accordance with plans and specifications approved by the Municipal Engineer or Municipality.
(3) 
Existing landscaping. Use of land for maintenance, replacement or enhancement of existing landscaping.
(4) 
Gardening. Use of land for gardening for home consumption.
(5) 
Agricultural related activities.
(a) 
Agricultural activities (as defined in Article II), when performed in accordance with the requirements of 25 PA Code Chapter 102.
(b) 
High Tunnel if:
[1] 
The High Tunnel or its flooring does not result in an impervious surface exceeding 25% of all structures located on the Landowner's total contiguous land area under common ownership; and
[2] 
The High Tunnel meets one of the following:
[a] 
The High Tunnel is located at least 100 feet from any perennial stream or watercourse, public road or neighboring property line.
[b] 
The High Tunnel is located at least 35 feet from any perennial stream or watercourse, public road or neighboring property line and located on land with a slope not greater than 7%.
[c] 
The High Tunnel is supported with a buffer or diversion system that does not directly drain into a stream or other watercourse by managing stormwater runoff in a manner consistent with the requirements of Pennsylvania Act 167.
(6) 
Forest management. Forest management operations, which are consistent with a sound forest management plan as filed with the Municipality and which comply with the Pennsylvania Department of Environmental Protection's management practices contained in its publication "Soil Erosion and Sedimentation Control Guidelines for Forestry" (as amended or replaced by subsequent guidance). Such operations are required to have an Erosion and Sedimentation Control Plan, which meets the requirements of 25 PA Code Chapter 102 and meets the erosion and sediment control standards of § 294-15 of this chapter.
(7) 
Maintenance of existing gravel and paved surfaces. Replacement of existing gravel and paved surfaces shall meet the erosion and sediment control requirements of 25 PA Code Chapter 102 and § 294-13E of this chapter, and is exempt from all other requirements of this chapter listed in Subsection H above. Resurfacing of existing gravel and paved surfaces is also exempt from the requirements of this chapter listed above. Paving of existing gravel surfaces is exempt from the requirements of this chapter listed above. Construction of new or additional Impervious Surfaces shall comply with all requirements of this chapter as indicated in Table 302.1.
(8) 
Municipal roadway shoulder improvements. Shoulder improvements conducted within the existing roadway cross-section of municipal owned roadways, unless an NPDES permit is required, in which case the proposed work must comply with all requirements of this chapter.
(9) 
In-place replacement of residential dwelling unit. The replacement in the exact footprint of an existing one- or two-family dwelling unit.
(10) 
In-place replacement, repair, or maintenance of residential impervious surfaces. The replacement of existing residential patios, decks, driveways, pools, garages, and/or sidewalks that are accessory to an existing one- or two-family dwelling unit in the exact footprint of the existing Impervious Surface.
H. 
Modified requirements for small projects.
(1) 
Regulated Activities that involve both of the following: 1) 240 to 2,500 square feet of Proposed Impervious Surfaces and 2) 1,000 to 5,000 square feet of proposed Earth Disturbance may apply the modified requirements presented in the "Simplified Approach to Stormwater Management for Small Projects" (Simplified Approach) (Appendix A) to comply with the requirements of §§ 294-13, 294-15, 294-16, 294-17, 294-18, 294-19, and 294-20, and Article IV, Article V, and Article VI of this chapter (as shown in Table 302.2). The Applicant shall first contact the Municipal Engineer: to confirm that the proposed project is eligible for use of the Simplified Approach and is not otherwise exempt from these Ordinance provisions; to determine what components of the proposed project are to be considered as Impervious Surfaces; and to determine if other known Site or local conditions exist that may preclude the use of any techniques included in the Simplified Approach. Appendix A includes instructions and procedures for preparation, submittal, review and approval of documents required when using the Simplified Approach and shall be adhered to by the Applicant. All other provisions of this chapter shall apply.
(2) 
Anyone proposing a small project shall submit 10 copies of the small project application to the Borough.
(3) 
A complete small project application shall include:
(a) 
Small project application form.
(b) 
Small project sketch plan, including the following:
[1] 
Name and address of landowner (and/or) developer.
[2] 
Date of small project application submission.
[3] 
Name of individual and/or firm that prepared the sketch if different than the landowner and/or developer.
[4] 
Location and square footage of proposed impervious area or land disturbance.
[5] 
Approximate footprint and location of all structures on adjacent properties if located within 50 feet of the proposed impervious area or land disturbance.
[6] 
Approximate location of existing stormwater management facilities, if present.
[7] 
Location and description of proposed stormwater management facilities.
[8] 
Direction of proposed stormwater discharge (e.g., with arrows).
[9] 
Scale and North arrow.
(c) 
Filing fee (in accordance with the Borough of Marietta's current fee schedule).
(4) 
The small project application shall be submitted in a format that is clear, concise, legible, neat and well organized.
TABLE 302.2
Thresholds for Regulated Activities that are Eligible for "Modified" Requirements for the Provisions of this chapter that are Listed Below
Ordinance Article/Section
Activities Listed in Subsection 302.I
Article I
All Provisions Apply
Article II
All Provisions Apply
§§ 294-22 and 294-13E
All Provisions Apply
§§ 294-13, 294-15, 294-16, 294-17, 294-18, and 294-19
Exempt if Modified Requirements of 294-14I are Applied
Article IV
Exempt if Modified Requirements of § 294-14I are Applied
Article V
Exempt if Modified Requirements of § 294-14I are Applied
Article VI
Exempt if Modified Requirements of § 294-14I are Applied
Article VII
Exempt if Modified Requirements of § 294-14I are Applied
Article VIII
All Provisions Apply
Other Erosion, Sediment and Pollution Control Requirements
Must comply with Title 25, Chapter 102 of the PA Code and other applicable State and municipal codes, including the Clean Streams Law.
Table 302.2 Notes:
•
"Modified Requirements" - Regulated Activities listed within the Subsections of this chapter noted in Table 302.2 are eligible for exemption only from the indicated sections and subsections of this chapter and only if the modified requirements of § 294-14I are met to the satisfaction of the Municipality; all other provisions of this chapter apply.
To control Post-construction stormwater impacts from Regulated Activities and meet State water quality requirements, BMPs shall be provided in the Site design that replicate Predevelopment stormwater infiltration and runoff conditions, such that Post-construction stormwater discharges do not degrade the physical, chemical, or biological characteristics of the receiving waters. The green infrastructure and Low Impact Development (LID) practices provided in the PA BMP Manual, as well as the guidance on green infrastructure LID and Conservation Design (CD) provided in Appendix B, shall be utilized for all regulated activities wherever possible. The Applicant shall comply with the following water quality and runoff volume requirements for all Regulated Activities, including all New Development and Redevelopment activities:
A. 
The Post-construction total runoff volume shall not exceed the Predevelopment total runoff volume for all storms equal to or less than the two year, 24-hour duration precipitation (design storm) or a minimum of 1.5 inches of runoff from all Regulated Impervious Surfaces shall be managed, whichever volume to be managed is greater. The water quality and runoff volume to be managed shall consist of any runoff volume generated by the proposed Regulated Activity over and above the Predevelopment total runoff volume and shall be captured and permanently retained or infiltrated on the Site. Permanent retention options may include, but are not limited to, reuse, evaporation, transpiration, and infiltration.
B. 
For modeling purposes, the Predevelopment ground cover conditions shall be determined using the corresponding ground cover assumptions presented in § 294-19D of this chapter.
C. 
The design of the Stormwater Management Facility outlet shall provide for protection from clogging and unwanted sedimentation.
D. 
BMPs that moderate the temperature of stormwater shall be used to protect the temperature of receiving waters.
E. 
Water quality improvement shall be achieved in conjunction with achieving the infiltration requirements of § 294-16. The infiltration volume required under § 294-16 may be included as a component of the water quality volume. If the calculated water quality and runoff volume is greater than the volume infiltrated, then the difference between the two volumes shall be managed for water quality and runoff volume control through other techniques or practices but shall not be discharged from the Site.
F. 
Runoff from the Disturbed Area shall be treated for water quality prior to entering existing waterways or water bodies. If a stormwater management practice does not provide water quality treatment, then water quality BMPs shall be utilized to provide pre-treatment prior to the runoff entering the stormwater management practice.
G. 
The Municipality may require additional water quality and runoff control measures for stormwater discharging to special management areas such as those listed in § 294-135.
H. 
When the Regulated Activity contains or is divided by multiple drainage areas, the water quality and runoff volume shall be separately addressed for each drainage area.
I. 
Weighted averaging of runoff coefficients shall not be used for manual computations or input data for water quality and runoff volume calculations.
J. 
Areas located outside of the Site (i.e., areas outside of the Regulated Activity) may be excluded from the calculation of the water quality and runoff volume requirements.
Providing for infiltration consistent with the natural hydrologic regime is required to compensate for the reduction in the recharge that occurs when the ground surface is disturbed or Impervious Surface is created or expanded. The Applicant shall achieve the following infiltration requirements:
A. 
For Regulated Activities involving either New Development or Redevelopment, infiltration should be designed to accommodate the entire water quality and runoff volume required in § 294-15. If the runoff volume required by § 294-15 cannot be infiltrated, then alternative methods consistent with the PA BMP Manual (as amended) may be used to manage this volume with approval from the Municipal Engineer. If the requirements of any subsection of § 294-16 cannot be physically accomplished, then the Applicant shall be responsible for demonstrating with data or calculations to the satisfaction of the Municipal Engineer why the required infiltration volume controls cannot be physically accomplished on the Site (e.g., shallow depth to bedrock or limiting zone, open voids, steep slopes, etc.) and what alternative volume can be infiltrated; however in all cases at least the first 0.5 inch of runoff volume shall be infiltrated.
B. 
A waiver from § 294-16 shall be considered by the Municipality only if a minimum of at least 0.5 inch infiltration requirement cannot be physically accomplished on the Site.
C. 
If Site conditions preclude capture of runoff from portions of the Impervious Surfaces, the infiltration volume for the remaining area shall be increased by an equivalent amount to offset the loss.
D. 
When a project contains or is divided by multiple watersheds, the infiltration volume shall be separately addressed for each watershed.
E. 
Existing Impervious Surfaces located in areas outside of the Site (i.e., outside of the Regulated Activity) may be excluded from the calculation of the required infiltration volume.
F. 
A detailed soils evaluation of the Site shall be conducted by a qualified professional and at a minimum shall address soil permeability, depth to bedrock, and subgrade stability. The general process for designing the infiltration BMP shall be conducted by a qualified Licensed Professional and shall be consistent with the PA BMP Manual (as amended) (or other guidance acceptable to the Municipal Engineer) and in general shall:
(1) 
Analyze hydrologic soil groups as well as natural and man-made features within the Site to determine general areas of suitability for infiltration practices. In areas where development on fill material is under consideration, conduct geotechnical investigations of sub-grade stability; infiltration may not be ruled out without conducting these tests.
(2) 
Provide field tests such as double ring infiltrometer or other hydraulic conductivity tests (at the elevation of the proposed infiltration surface) to determine the appropriate hydraulic conductivity rate. Standard septic/sewage percolation tests are not acceptable for design purposes.
(3) 
Design the Infiltration Facility for the required retention (infiltration) volume based on field-determined infiltration capacity (and apply safety factor as per applicable design guidelines) at the elevation of the proposed infiltration surface.
(4) 
On-lot infiltration features are encouraged; however, it shall be demonstrated to the Municipal Engineer that the soils are conducive to infiltration on the identified lots.
G. 
Infiltration BMPs shall be selected based on suitability of soils and Site conditions and shall be constructed on soils that have the following characteristics:
(1) 
A minimum depth of 24 inches between the bottom of the BMP and the top of the Limiting Zone. Additional depth may be required in areas underlain by Karst or carbonate geology.
(2) 
An infiltration rate sufficient to accept the additional stormwater volume and drain completely as determined by field tests conducted by the Applicant.
(3) 
The Infiltration Facility shall completely drain the retention (infiltration) volume within three days (72 hours) from the end of the design storm.
H. 
All infiltration practices shall:
(1) 
Be set back at least 25 inches from all buildings and features with sub-grade elements (e.g., basements, foundation walls, etc.), unless otherwise approved by the Municipal Engineer;
(2) 
For any infiltration practice that collects runoff from shared or multiple features and that is located within 50 feet of a building or feature with sub-grade elements (e.g., basements, foundation walls, etc.), the bottom elevation shall be set below the elevation of the sub-grade element.
I. 
Infiltration Facilities shall, to the maximum extent practicable, be located to avoid introducing contaminants to groundwater:
(1) 
When a Hotspot is located in the area draining to a proposed Infiltration Facility, an evaluation of the potential of groundwater contamination from the proposed Infiltration Facility shall be performed, including a hydrogeologic investigation (if necessary) by a qualified Licensed Professional to determine what, if any, pretreatment or additional design considerations are needed to protect groundwater quality.
(2) 
When located within a "well head protection area" of a public water supply well, infiltration practices shall be in conformance with the applicable approved source water protection assessment or source water protection plan.
(3) 
The Applicant shall provide appropriate safeguards against groundwater contamination for land uses that may cause groundwater contamination should there be a mishap or spill.
J. 
During Site construction, all infiltration practice components shall be protected from compaction due to heavy equipment operation or storage of fill or construction material. Infiltration areas shall also be protected from sedimentation. Areas that are accidentally compacted or graded shall be remediated to restore soil composition and porosity. Adequate documentation to this effect shall be submitted to the Municipal Engineer for review. All areas designated for infiltration shall not receive runoff until the contributory drainage area has achieved final stabilization.
K. 
Where sediment transport in the stormwater runoff is anticipated to reach the infiltration system, appropriate permanent measures to prevent or collect sediment shall be installed prior to discharge to the infiltration system.
L. 
Where roof drains are designed to discharge to infiltration practices, they shall have appropriate measures to prevent clogging by unwanted debris (for example, silt, leaves and vegetation). Such measures shall include but are not limited to leaf traps, gutter guards and cleanouts.
M. 
All infiltration practices shall have appropriate positive overflow controls.
N. 
No sand, salt or other particulate matter may be applied to a porous surface material for winter ice conditions.
O. 
The following procedures and materials shall be required during the construction of all subsurface facilities:
(1) 
Excavation for the Infiltration Facility shall be performed with equipment that will not compact the bottom of the seepage bed/trench or like facility.
(2) 
The bottom of the bed and/or trench shall be scarified prior to the placement of aggregate.
(3) 
Only clean aggregate with documented porosity, free of fines, shall be allowed.
(4) 
The tops, bottoms and sides of all seepage beds, trenches, or like facilities shall be covered with drainage fabric. Fabric shall be non-woven fabric acceptable to the Municipal Engineer.
(5) 
Stormwater shall be distributed throughout the entire seepage bed/trench or like facility and provisions for the collection of debris shall be provided in all facilities.
For Regulated Activities involving New Development with one or more acres of Earth Disturbance, the Applicant shall comply with the following stream channel protection requirements to minimize stream channel erosion and associated water quality impacts to the receiving waters:
A. 
The peak flow rate of the Post-construction two year, 24-hour design storm shall be reduced to the Predevelopment peak flow rate of the one year, 24-hour duration precipitation, using the SCS Type II distribution.
B. 
To the maximum extent practicable, and unless otherwise approved by the Municipal Engineer, the Post-construction one year, 24-hour storm flow shall be detained for a minimum of 24 hours and a maximum not to exceed 72 hours from a point in time when the maximum volume of water from the one year, 24-hour storm is stored in a proposed BMP (i.e., when the maximum water surface elevation is achieved in the facility). Release of water can begin at the start of the storm (i.e., the invert of the orifice is at the invert of the proposed BMP).
C. 
For modeling purposes, the Predevelopment ground cover conditions shall be determined using the corresponding ground cover assumptions presented in § 294-19D of this chapter.
D. 
The minimum orifice size in the outlet structure to the BMP shall be three inches in diameter unless otherwise approved by the Municipal Engineer, and a trash rack shall be installed to prevent clogging. For Sites with small drainage areas contributing to the BMP that do not provide enough runoff volume to allow a 24-hour attenuation with the three-inch orifice, the calculations shall be submitted showing this condition.
E. 
When the calculated orifice size is below three inches, gravel filters (or other methods) are recommended to discharge low-flow rates subject to the Municipal Engineer's satisfaction. When filters are utilized, maintenance provisions shall be provided to ensure filters meet the design function.
F. 
All proposed Stormwater Management Facilities shall make use of measures to extend the flow path and increase the travel time of flows in the facility.
G. 
When a Regulated Activity contains or is divided by multiple drainage areas, the peak flow rate control shall be separately addressed for each drainage area.
The Applicant shall comply with the following peak flow rate control requirements for all Regulated Activities including those that involve New Development and Redevelopment.
A. 
Post-construction peak flow rates from any Regulated Activity shall not exceed the Predevelopment peak flow rates as shown for each of the design storms specified in Table 306.1.
Table 306.1
Peak Rate Control Standards
(Peak Flow Rate of the Post-construction Design Storm shall be Reduced to the Peak Flow Rate of the Corresponding Predevelopment Design Storm Shown in the Table)
Post-Construction Design Storm Frequency (24-Hour Duration)
Pre Development Design Storm
New Development Regulated Activities
Redevelopment Regulated Activities
2-Year
1-Year
2-Year
5-Year
5-Year
5-Year
10-Year
10-Year
10-Year
25-Year
25-Year
25-Year
50-Year
50-Year
50-Year
100-Year
100-Year
100-Year
B. 
For modeling purposes, the Predevelopment ground cover conditions shall be determined using the corresponding ground cover assumptions presented in § 294-19D of this chapter.
C. 
For Regulated Activities involving only Redevelopment, no peak flow rate controls are required when and only if the total Proposed Impervious Surface area is at least 20% less than the total existing Impervious Surface area to be disturbed by the Regulated Activity. In all cases where this requirement is not met, the Redevelopment Regulated Activity shall achieve the peak flow rate controls presented in Table 306.1, using the Redevelopment Ground Cover Assumptions presented in § 294-19D. This design criterion for Redevelopment is only permitted with approval of Municipal Engineer. It shall result in no measurable impact on downstream properties.
D. 
Only the area of the proposed Regulated Activity shall be subject to the peak flow rate control standards of this chapter. Undisturbed areas for which the discharge point has not changed are not subject to the peak flow rate control standards.
E. 
Areas located outside of the Site (i.e., areas outside of the Regulated Activity) that drain through a proposed Site are not subject to peak flow rate control requirements. Drainage facilities located on the Site shall be designed to safely convey flows from outside of the Site through the Site.
F. 
When a Regulated Activity contains or is divided by multiple drainage areas, the peak flow rate controls shall be separately addressed for each drainage area.
G. 
The effect of structural and non-structural stormwater management practices implemented as part of the overall Site design may be taken into consideration when calculating total storage volume and peak flow rates.
A. 
Stormwater runoff from all Regulated Activity Sites with a drainage area of greater than five acres shall be calculated using a generally accepted calculation technique(s) that is based on the NRCS Soil Cover Complex Method. Table 307.1 summarizes acceptable computation methods. The method selected for use shall be based on the individual limitations and suitability of each method for a particular Site. The use of the Rational Method to estimate peak discharges for drainage areas greater than five acres shall be permitted only upon approval by the Municipal Engineer.
Table 307.1
Acceptable Computation Methodologies for SWM Site Plan
Method
Developed By
Applicability
TR-20
(or commercial computer package based on TR-20)
USDA NRCS
Applicable where use of full hydrology computer model is desirable or necessary.
TR-55
(or commercial computer package based on TR-55)
USDA NRCS
Applicable for land development plans where limitations described in TR55 are met.
HEC-1/HEC-HMS
US Army Corps of Engineers
Applicable where use of a full hydrologic computer model is desirable or necessary.
Rational Method (or commercial computer package based on Rational Method)
Emil Kuichling (1889)
For Sites up to five acres, or as approved by the Municipality.
Other Methods
Varies
Other computation methodologies approved by the Municipality.
B. 
All calculations using the Soil Cover Complex Method shall use the appropriate design rainfall depths for the various return period storms consistent with this chapter. Rainfall depths used shall be obtained from NOAA Atlas 14 values consistent with a partial duration series. When stormwater calculations are performed for routing procedures or infiltration, water quality and runoff volume functions, the duration of rainfall shall be 24 hours.
C. 
All calculations using the Rational Method shall use rainfall intensities consistent with appropriate times-of-concentration (duration) and storm events with rainfall intensities obtained from NOAA Atlas 14 partial duration series estimates, or the latest version of the PennDOT Drainage Manual (PDM Publication 584). Times-of-concentration shall be calculated based on the methodology recommended in the respective model used. Times of concentration for channel and pipe flow shall be computed using Manning's equation.
D. 
The Applicant shall utilize the following ground cover assumptions for all Predevelopment water quality and runoff volume, infiltration volume and peak flow rate calculations:
(1) 
For Regulated Activities involving New Development, the following ground cover assumptions shall be used:
(a) 
For areas that are Woods (as defined in Article II of this chapter), predevelopment calculations shall assume ground cover of "Woods in good condition."
(b) 
For all other areas (including all Impervious Surfaces), Predevelopment calculations shall assume ground cover of "meadow."
(2) 
For Regulated Activities involving Redevelopment, the following ground cover assumptions shall be used:
(a) 
For areas that are Woods (as defined in Article II of this chapter), Predevelopment calculations shall assume ground cover of "Woods in good condition."
(b) 
For areas that are not Woods or not Impervious Surfaces, Predevelopment calculations shall assume ground cover of "meadow."
(c) 
For areas that are Impervious Surfaces, Predevelopment calculations shall assume at least 20% of the existing Impervious Surface area to be disturbed as "meadow" ground cover.
(3) 
The Applicant shall determine which stormwater standards apply to the proposed Regulated Activity as follows:
(a) 
Stormwater standards for New Development shall apply to all proposed Regulated Activities that involve only New Development activities as defined in this chapter.
(b) 
Stormwater standards for Redevelopment shall apply to all proposed Regulated Activities that involve only Redevelopment activities as defined in this chapter.
(c) 
At the discretion of the Municipal Engineer, Regulated Activities that involve a combination of both New Development and Redevelopment activities, as defined in this chapter, may either:
[1] 
Apply the stormwater standards (Redevelopment or New Development) that are associated with the activity that involves the greatest amount of land area; or
[2] 
Apply the Redevelopment and New Development stormwater standards to the corresponding Redevelopment and New Development portions of the proposed Regulated Activity.
E. 
Runoff curve numbers (CN) for both Predevelopment and proposed (Post-construction) conditions to be used in the Soil Cover Complex Method shall be obtained from Table C-1 in Appendix B of this chapter.
F. 
Runoff coefficients (C) for both Predevelopment and proposed (Post-construction) conditions for use in the Rational Method shall be obtained from Table C-2 in Appendix B of this chapter.
G. 
Weighted averaging of runoff coefficients shall not be used for manual computations or input data for water quality and runoff volume calculations.
H. 
Hydraulic computations to determine the capacity of pipes, culverts, and storm sewers shall be consistent with methods and computations contained in the Federal Highway Administration Hydraulic Design Series Number 5 (Publication No. FHWA-NHI-01-020 HDS No. 5, as amended). Hydraulic computations to determine the capacity of open channels shall be consistent with methods and computations contained in the Federal Highway Administration Hydraulic Engineering Circular Number 15 (Publication No. FHWA-NHI-05-114 HEC 15, as amended). Values for Manning's roughness coefficient (n) shall be consistent with Table C-3 in Appendix B of the Ordinance.
I. 
Runoff calculations shall include the following assumptions:
(1) 
Average antecedent moisture conditions (for the Soil Cover Complex Method only for example, TR-55, TR-20).
(2) 
A type II distribution storm (for the Soil Cover Complex Method only for example, TR-55, TR-20).
A. 
Any stormwater basin required or regulated by this chapter designed to store runoff and requiring a berm or earthen embankment shall be designed to provide an emergency spillway to safely convey flow up to and including the 100-year proposed conditions. The height of embankment shall provide a minimum one foot of Freeboard above the maximum pool elevation computed when the facility functions for the 100-year proposed conditions inflow. Should any BMP require a dam safety permit under PA Chapter 105 regulations, the facility shall be designed in accordance with and meet the regulations of PA Chapter 105 concerning dam safety. PA Chapter 105 may require the safe conveyance of storms larger than 100-year event.
B. 
Any drainage Conveyance facility and/or channel not governed by PA Chapter 105 regulations shall be designed to convey, without damage to the drainage facility or roadway, runoff from the 25-year storm event. Larger storm events 50-year and 100-year storms) shall also be safely conveyed in the direction of natural flow without creating additional damage to any drainage facilities, nearby structures, or roadways.
C. 
Conveyance facilities to or exiting from stormwater management facilities (i.e., detention basins) shall be designed to convey the design flow to or from the facility.
D. 
Roadway crossings or structures located within designated floodplain areas shall be able to convey runoff from a 100-year design storm consistent with Federal Emergency Management Agency National Flood Insurance Program - Floodplain Management Requirements.
E. 
Any Stormwater Management Facility located within a PennDOT right-of-way shall comply with PennDOT minimum design standards and permit submission and approval requirements.
F. 
Adequate erosion protection and energy dissipation shall be provided along all open channels and at all points of discharge. Design methods shall be consistent with the Federal Highway Administration Hydraulic Engineering Circular Number 11 (Publication No. FHWA-IP-89-016, as amended) and the PADEP Erosion and Sediment Pollution Control Program Manual (Publication No. 363-2134-008, as amended), or other design guidance acceptable to the Municipal Engineer.
A. 
In order to protect and improve water quality, a Riparian Buffer Easement shall be created and recorded as part of any subdivision or land development that encompasses a Riparian Buffer. Riparian Buffer Easement Agreements shall be submitted to the Municipality's Solicitor for review and approval prior to recording.
B. 
Except as required by Chapter 102, the Riparian Buffer Easement shall be measured to be the greater of the limit of the 100-year floodplain or a minimum of 35 feet from the top of the streambank (on each side).
C. 
Minimum management requirements for riparian buffers.
(1) 
Existing native vegetation shall be protected and maintained within the Riparian Buffer Easement.
(2) 
Whenever practicable, invasive vegetation shall be actively removed and the Riparian Buffer Easement shall be planted with native trees, shrubs and other vegetation to create a diverse native plant community appropriate to the intended ecological context of the site.
D. 
The Riparian Buffer Easement shall be enforceable by the Municipality and shall be recorded in the appropriate County Recorder of Deeds Office, so that it shall run with the land and shall limit the use of the property located therein. The easement shall allow for the continued private ownership and shall count toward the minimum lot area required by Zoning, unless otherwise specified in the municipal Zoning Ordinance.
E. 
Any permitted use within the Riparian Buffer Easement shall be conducted in a manner that will maintain the extent of the existing 100-year floodplain, improve or maintain the stream stability, and preserve and protect the ecological function of the floodplain.
F. 
The following conditions shall apply when public and/or private recreation trails are permitted within Riparian Buffers:
(1) 
Trails shall be for non-motorized use only.
(2) 
Trails shall be designed to have the least impact on native plant species and other sensitive environmental features.
G. 
Septic drainfields and sewage disposal systems shall not be permitted within the Riparian Buffer Easement and shall comply with setback requirements established under 25 Pa. Code Chapter 73.
The following permit or other regulatory requirements may apply to certain Regulated Activities and shall be met prior to (or as a condition of) final approval by the Municipality of the SWM Site Plan and prior to commencement of any Regulated Activities, as applicable:
A. 
All Regulated Activities subject to permit or regulatory requirements by PADEP under regulations at Title 25 Pennsylvania Code Chapter 102, or erosion and sediment control requirements of the Municipality.
B. 
Work within natural drainage ways subject to permit by PADEP under Title 25 Pennsylvania Code Chapter 105.
C. 
Any BMP or Conveyance that would be located in or adjacent to surface Waters of the Commonwealth, including wetlands, subject to permit by PADEP under Title 25 Pennsylvania Code Chapter 105.
D. 
Any BMP or Conveyance that would be located on or discharge to a State highway right-of-way, or require access to or from a State highway and be subject to approval by PennDOT.
E. 
Culverts, bridges, storm sewers, or any other facilities which must pass or convey flows from the tributary area and any facility which may constitute a dam subject to permit by PADEP under Title 25 Pennsylvania Code Chapter 105.
To control Post-construction stormwater impacts from Regulated Activities and meet State water quality requirements, BMPs shall be provided in the Site design that replicate Predevelopment stormwater infiltration and runoff conditions, such that Post-construction stormwater discharges do not degrade the physical, chemical, or biological characteristics of the receiving waters. The green infrastructure and Low Impact Development (LID) practices provided in the PA BMP Manual, as well as the guidance on green infrastructure LID and Conservation Design (CD) provided in Appendix B, shall be utilized for all regulated activities wherever possible. The Applicant shall comply with the following water quality and runoff volume requirements for all Regulated Activities, including all New Development and Redevelopment activities:
A. 
The Post-construction total runoff volume shall not exceed the Predevelopment total runoff volume for all storms equal to or less than the two-year, 24-hour duration precipitation (design storm) or a minimum of 1.5 inches of runoff from all Regulated Impervious Surfaces shall be managed, whichever volume to be managed is greater. The water quality and runoff volume to be managed shall consist of any runoff volume generated by the proposed Regulated Activity over and above the Predevelopment total runoff volume and shall be captured and permanently retained or infiltrated on the Site. Permanent retention options may include, but are not limited to, reuse, evaporation, transpiration, and infiltration.
B. 
For modeling purposes, the Predevelopment ground cover conditions shall be determined using the corresponding ground cover assumptions presented in § 294-19D of this chapter.
C. 
The design of the Stormwater Management Facility outlet shall provide for protection from clogging and unwanted sedimentation.
D. 
BMPs that moderate the temperature of stormwater shall be used to protect the temperature of receiving waters.
E. 
Water quality improvement shall be achieved in conjunction with achieving the infiltration requirements of § 294-15. The infiltration volume required under § 294-15 may be included as a component of the water quality volume. If the calculated water quality and runoff volume is greater than the volume infiltrated, then the difference between the two volumes shall be managed for water quality and runoff volume control through other techniques or practices but shall not be discharged from the Site.
F. 
Runoff from the Disturbed Area shall be treated for water quality prior to entering existing waterways or water bodies. If a stormwater management practice does not provide water quality treatment, then water quality BMPs shall be utilized to provide pre-treatment prior to the runoff entering the stormwater management practice.
G. 
The Municipality may require additional water quality and runoff control measures for stormwater discharging to special management areas such as those listed in § 294-13R.
H. 
When the Regulated Activity contains or is divided by multiple drainage areas, the water quality and runoff volume shall be separately addressed for each drainage area.
I. 
Weighted averaging of runoff coefficients shall not be used for manual computations or input data for water quality and runoff volume calculations.
J. 
Areas located outside of the Site (i.e., areas outside of the Regulated Activity) may be excluded from the calculation of the water quality and runoff volume requirements.
A. 
Aboveground storage facilities.
(1) 
Aboveground storage facilities consist of all stormwater facilities which store, infiltrate/evaporate/transpire, clean or otherwise affect stormwater runoff and the top of which is exposed to the natural environment. Aboveground storage facilities are located above the finished ground elevation. Aboveground storage facilities do not include stormwater management facilities designed for conveyance or cisterns.
(2) 
Design criteria. Aboveground storage facilities shall comply with the design criteria in the following table:
Aboveground Storage Facility Design Criteria Facility Depth
Less than 2 Feet
2 Feet to 8 Feet
Greater than 8 Feet
Embankment geometry
Top width (minimum)
2 feet
5 feet
10 feet
Interior side slope (maximum)
2:1
3:1
5:1
Exterior side slope (maximum)
2:1
3:1
3:1
Embankment construction
Key trench
Not required
Required
Required
Pipe collar
Not required
Required
Required
Compaction density
Not required
Required
Required
Internal construction
Dewatering feature
N/A
Required
Required
Pretreatment elements
Not required*
Required
Required
Outlet structure
Pipe size (minimum)
6 inches
15 inches
15 inches
Pipe material
SLHDPE, PVC, RCP
SLHDPE, RCP
RCP
Anticlogging devices
Required
Required
Required
Antivortex design
Not required
Required
Required
Watertight joints in piping?
No
Yes
Yes
Spillway Requirements
Spillway freeboard (minimum)
Not required
6 inches
12 inches
Width (minimum)
Not required
10 feet
20 feet
Width (maximum)
Not required
50 feet
50 feet
Spillway channel design
Required
Required
Required
Routing of 100-year storm
Permitted
Permitted
Permitted
Notes:
* Pretreatment required for infiltration BMPs unless shown to be unnecessary
N/A
=
Not applicable
SLHDPE
=
Smooth-lined high-density polyethylene pipe; PVC = Polyvinyl chloride
RCP
=
Reinforced concrete pipe
B. 
Facility depth.
(1) 
For the purposes of the design criteria, the facility depth is defined to be the depth between the bottom invert of the lowest orifice and the invert of the spillway. If there is no spillway, the top of the berm shall be used. For basins with no orifices or outlet structure, the bottom elevation of the basin shall be used.
(2) 
Facilities with a facility depth greater than eight feet shall not be permitted.
C. 
Embankment construction.
(1) 
Impervious core/key trench. An impervious core/key trench, when required, shall consist of a cutoff trench (below existing grade) and a core trench (above existing grade). A key trench may not be required wherever it can be shown that another design feature, such as the use of an impermeable liner, accomplishes the same purpose.
(2) 
Materials. Materials used for the core shall conform to the Unified Soil Classification GC, SC, CH, or CL and must have at least 30% passing the No. 200 sieve.
(3) 
Dimensions. The dimensions of the core shall provide a minimum trench depth of two feet below existing grade, minimum width of four feet and side slope of 1H:1V or flatter. The core should extend up both abutments to the 10-year water surface elevation or six inches below the emergency spillway elevation, whichever is lower. The core shall extend four feet below any pipe penetrations through the impervious core. The core shall be installed along or parallel to the center line of the embankment.
(4) 
Compaction. Compaction requirements shall be the same as those for the embankment to assure maximum density and minimum permeability. The core shall be constructed concurrently with the outer shell of the embankment. The trench shall be dewatered during backfilling and compaction operations.
(5) 
Pipe collars. All pipe collars, when required, shall be designed in accordance with Chapter 7 of the DEP E&S Manual. The material shall consist of concrete or otherwise nondegradable material around the outfall barrel and shall be watertight.
(6) 
Embankment fill material. The embankment fill material shall be taken from an appropriate borrow area which shall be free of roots, stumps, wood, rubbish, stones greater than six inches, frozen or other objectionable materials.
(7) 
Embankment compaction. When required, embankments shall be compacted by sheepsfoot or pad roller. The loose lift thickness shall be nine inches or less, depending on roller size, and the maximum particle size is six inches or less (2/3 of the lift thickness). Five passes of the compaction equipment over the entire surface of each lift is required. Embankment compaction to visible nonmovement is also required.
(8) 
Internal construction.
(a) 
Bottom slope. The minimum bottom slope of facilities not designed for infiltration shall be 1%. A flatter slope may be used if an equivalent dewatering mechanism is provided.
(b) 
Dewatering features. When required, dewatering shall be provided through the use of underdrain, surface device, or alternate approved by the Borough Engineer. If the facility is to be used for infiltration, the dewatering device should be capable of being disconnected and only be made operational if the basin is not dewatering within the required time frame.
(9) 
Pretreatment elements. When required, pretreatment elements shall consist of forebays, or alternate approved by the Borough Engineer, to keep silt to a smaller portion of the facility for ease of maintenance.
(10) 
Infiltration basins. Within basins designed for infiltration, existing native vegetation shall be preserved, if possible. For existing unvegetated areas or for infiltration basins that require excavation, a planting plan shall be prepared in accordance with § 294-13N and the PA BMP Manual which is designed to promote infiltration.
(11) 
Outlet configuration:
(a) 
For facilities with a depth of two feet or greater, a type D-W endwall or riser box outlet structure shall be provided.
(b) 
For facilities with a depth less than two feet, at the discretion of the Borough Engineer.
(c) 
All discharge control devices with appurtenances shall be made of reinforced concrete and stainless steel. Bolts/fasteners shall be stainless steel.
(12) 
Spillway.
(a) 
Material. The spillway shall be designed to provide a nonerosive, stable condition when the project is completed.
(b) 
Nonemergency use. Use of the spillway to convey flows greater than the 50-year design storm is permitted.
(c) 
Emergency use. The spillway shall be designed to convey the 100-year peak inflow. When required, freeboard shall be measured from the top of the water surface elevation for emergency use.
(d) 
Breach analysis. The Borough may require a breach analysis based on site-specific conditions and concern of threat for downstream property. When required, the breach analysis shall be conducted in accordance with the NRCS methodology, the United States Army Corps of Engineers methodology (HEC-1) or other methodologies as approved by the Borough.
D. 
Subsurface storage facilities. Subsurface storage facilities consist of all stormwater facilities which store, infiltrate/evaporate/transpire, clean or otherwise affect stormwater runoff and the top of which is not exposed to the natural environment. Subsurface facilities are located below the finished ground elevation. Subsurface facilities do not include stormwater management facilities designed for conveyance. Design criteria. Subsurface storage facilities shall comply with the design criteria in the following table:
Subsurface Storage Facility Design Criteria
Facility Type
Infiltration with Storage
Storage Without Infiltration
Facility geometry
Depth from surface (maximum)
2 feet less than limiting zone
N/A
Loading ratio (maximum)
Per PA BMP Manual*
N/A
Distribution system requirements
Pipe size (minimum)
6 inches
6 inches
Pretreatment
Required
Required
Loading/balancing
Required
Not required
Observation/access ports
Required
Required
Notes:
*
Unless otherwise determined by professional geologic evaluation.
(1) 
Distribution system requirements.
(a) 
Pretreatment requirements. The facility shall be designed to provide a method to eliminate solids, sediment, and other debris from entering the subsurface facility.
(b) 
Loading/balancing. The facility shall be designed to provide a means of evenly balancing the flow across the surface of the facility to be used for infiltration.
(2) 
Observation/access ports. For facilities with the bottom less than five feet below the average grade of the ground surface, a cleanout shall be an acceptable observation port. For facilities with the bottom five feet or more below the average grade of the ground surface, a manhole or other means acceptable to the Borough shall be provided for access to and monitoring of the facility. The number of access points shall be sufficient to flush or otherwise clean out the system.
(3) 
Materials.
(a) 
Pipe material. Distribution system piping may be PVC, SLHDPE, or RCP.
(b) 
Stone for infiltration beds. The stone used for infiltration beds shall be clean washed, uniformly graded coarse aggregate (AASHTO No. 3 or equivalent approved by the Borough). The void ratio for design shall be assumed to be 0.4.
(c) 
Backfill material. Material consistency and placement depths for backfill shall be (at a minimum) per all applicable pipe manufacturer's recommendations, further providing it should be free of large (not exceeding six inches in any dimension) objectionable or detritus material. Select nonaggregate material should be indigenous to the surrounding soil material for nonvehicular areas. Backfill within vehicular areas shall comply with this section unless otherwise specified in Borough's Zoning or Subdivision and Land Development Ordinances. Furthermore, if the design concept includes the migration of runoff through the backfill to reach the infiltration facility, the material shall be well drained, free of excess clay or clay-like materials and generally uniform in gradation.
(d) 
Lining material. Nonwoven geotextiles shall be placed on the sides and top of subsurface infiltration facilities. No geotextiles shall be placed on the bottom of subsurface infiltration facilities.
(4) 
Cover. When located under pavement, the top of the subsurface facility shall be a minimum of six inches below the bottom of pavement subbase. Where located under vegetative cover, the top of the subsurface facility shall be a minimum of 12 inches below the surface elevation or as required to establish vegetation. Subsurface facilities shall be designed to safely convey and/or bypass flows from storms exceeding the design storm.
(5) 
Conveyance facilities.
(a) 
Conveyance facilities consist of all stormwater facilities which carry flow, which may be located either above or below the finished grade. Conveyance facilities do not include stormwater management facilities which store, infiltrate/evaporate/transpire, or clean stormwater runoff.
(b) 
Design criteria. Conveyance facilities shall comply with the design criteria in the following table:
Conveyance facility design criteria
Location
Within Public Street Right-of-Way
Outside Public Street Right-of-Way
Loading
All
Vehicular Loading
Nonvehicular Loading
Pipe design
Material
SLHDPE, RCP
PVC, SLHDPE, RCP
PVC, SLHDPE, RCP
Slope (minimum)
1.0%
1.0%
1.0%
Cover
1 foot to stone subgrade
1 foot to stone subgrade
1 foot to surface
Diameter (minimum)
15 inches
15 inches
15 inches
Street crossing angle
75° to 90°
N/A
N/A
Access/maintenance port frequency (maximum)
400 feet
400 feet
600 feet
Inlet design
Material
Concrete
Concrete
N/A
Grate depression
2 inches
2 inches
1 inch minimum
Manhole design
Material
Concrete
Concrete
Concrete
Swale design
Freeboard (minimum)
6 inches
N/A
6 inches
Velocity (maximum)
Stability check
N/A
Stability check
Slope (minimum)
1%
N/A
1%
Side slopes (residential
4:1 max area)
N/A
4:1 max
Side slopes (nonresidential 3:1 max area)
N/A
3:1 max
Bottom width to flow depth 12:1 ratio
N/A
12:1
Outlet design
End treatment
Headwall/endwall
N/A
Headwall/endwall or flared end section
Energy dissipater
Required
N/A
Required
Notes:
N/A
=
Not applicable or no criteria specified
SLHDPE
=
Smooth-lined high-density polyethylene pipe
PVC
=
polyvinyl chloride
RCP
=
Reinforced concrete pipe
(6) 
Conveyance pipes, culverts, manholes, inlets and endwalls within the public street right-of-way or proposed for dedication shall conform to the requirements of PennDOT Standards for Roadway Construction, Publication No. 72M. Conveyance pipes, culverts, manholes, inlets and endwalls which are otherwise subject to vehicular loading shall be designed for the HS-25 loading condition.
(7) 
Conveyance pipes.
(a) 
Backfill material consistency and placement depths for backfill shall be (at a minimum) per all applicable pipe manufacturer's recommendations, further providing it should be free of large (not exceeding six inches in any dimension) objectionable or detritus material. Select nonaggregate material should be indigenous to the surrounding soil material for nonvehicular areas. Backfill within vehicular areas shall comply with this section unless otherwise specified in the Borough's Zoning or Subdivision and Land Development Ordinances.
(b) 
Inlets or manholes shall be placed at all points of changes in the horizontal or vertical directions of conveyance pipes. Curved pipe sections are prohibited.
(c) 
Access/maintenance ports. An access/maintenance port is required and may either be an inlet or manhole.
(d) 
Watertight joints shall be provided where pipe sections are joined, except for perforated pipe installed as pavement base drain.
(e) 
The street crossing angle shall be measured between the pipe center line and the street center line.
(f) 
Elliptical pipe of an equivalent cross-sectional area may be substituted in lieu of circular pipe where cover or utility conflict conditions exist.
(g) 
The roughness coefficient (Manning "n" values) used for conveyance pipe capacity calculations should be determined in accordance with PennDOT Publication 584, PennDOT Drainage Manual, or per the manufacturer's specifications.
(8) 
Inlets.
(a) 
All pipes must enter inlets completely through one of the sides. No corner entry of pipes is permitted.
(b) 
Within the public street right-of-way, the gutter spread based on the 25-year storm shall be no greater than 1/2 of the travel lane and have a maximum depth of three inches at the curbline. A parking lane shall not be considered as part of the travel lane. In the absence of pavement markings separating a travel lane from the parking lane, the parking lane shall be assumed to be seven feet wide if parking is permitted on the street.
(c) 
Flow depth within intersections. Within intersections of streets, the maximum depth of flow shall be 1 1/2 inches based on the 25-year storm.
(9) 
Curbed streets.
(a) 
Inlets in streets shall be located along the curbline.
(b) 
Top units shall be PennDOT Type "C." The hood shall be aligned with the adjacent curb height.
(c) 
All inlets placed in paved areas shall have heavy duty bicycle-safe grating consistent with PennDOT Publication 72M, latest edition. A note to this effect shall be added to the SWM site plan or inlet details therein.
(d) 
Inlets, junction boxes, or manholes greater than five feet in depth shall be equipped with ladder rungs and shall be detailed on the SWM site plan.
(10) 
Swales.
(a) 
A swale shall be considered as any man-made ditch designed to convey stormwater directly to another stormwater management facility or surface waters.
(b) 
Inlets within swales shall have PennDOT Type "M" top units or equivalent approved by the Borough Engineer.
(c) 
Swale capacities and velocities shall be computed using the Manning equation using the following design parameters:
[1] 
Vegetated swales. The first condition shall consider swale stability based upon a low degree of retardance ("n" = 0.03); the second condition shall consider swale capacity based upon a higher degree of retardance ("n" = 0.05); and all vegetated swales shall have a minimum slope of 1% unless otherwise approved by the Borough Engineer.
[2] 
The "n" factors to be used for paved or riprap swales or gutters shall be based upon accepted engineering design practices, as approved by the Borough Engineer.
[3] 
All swales shall be designed to maximize infiltration and concentrate low flows to minimize siltation and meandering, unless geotechnical conditions do not permit infiltration.
[4] 
Culverts. In addition to the material requirements in this section, culverts designed to convey waters of the commonwealth may be constructed with either a corrugated metal arch or a precast concrete culvert.
[5] 
Level spreaders. Shall discharge at existing grade onto undisturbed vegetation. Discharge at a depth not exceeding 3.0 inches for a 100-year, 24-hour design storm.
[6] 
Energy dissipaters. Energy dissipaters shall be designed in accordance with the requirements in the DEP E&S Manual.
(11) 
End treatments.
(a) 
Where the connecting pipe has a diameter 15 inches or greater, headwalls and endwalls shall be provided with a protective barrier device to prevent entry of the storm sewer pipe by unauthorized persons. Such protection devices shall be designed to be removable for cleaning.
(b) 
Headwalls and endwalls shall be constructed of concrete.
(c) 
Flared end sections shall be of the same material as the connecting pipe and be designed for the size of the connecting pipe.
(12) 
SWM facilities which qualify as a dam per DEP regulations or facilities deemed a potential threat to the life, safety or welfare of the general public shall be subject to the following requirements:
(a) 
Facilities which qualify as a dam per DEP regulation shall obtain the required permit through DEP and design the facility in accordance with DEP standards.
(b) 
Additional requirements and analysis may be required by the Borough to prove that the proposed facility has been designed to limit the potential risk to the life, safety or welfare of the general public.