[Amended 2-18-2016]
Low-impact development (LID) techniques must be incorporated into redevelopment projects in the Town Center Overlay District. Applicants must use decentralized systems that involve the placement of a number of small treatment and infiltration devices located close to the various impervious surfaces that generate stormwater runoff in place of a centralized system comprised of closed pipes that direct all drainage from the entire site into one large detention basin. The following standards must be followed in the design of LID techniques.
A.
Stormwater recharge.
(1)
The volume of water to be recharged shall be calculated using existing site conditions and the infiltration rates set forth below:
Hydrologic Soil Group | Quantity to Recharge (inches of runoff) | |
|---|---|---|
A | 0.6 | |
B | 0.35 | |
C | 0.25 | |
D | 0.10 |
(2)
The volume of runoff to be recharged shall be calculated as follows:
Recharge Volume (ft3) = Impervious Area (ft2) X Quantity to Recharge (inches)/12 |
(3)
The following criteria also apply:
(a)
Initial exfiltration during the design storm shall not be accounted for during the unit/device sizing, with the exception of roof runoff devices, which may account for exfiltration in sizing calculations.
(b)
All units/devices shall be designed to drain completely with no standing water within 72 hours from the end of the storm.
(c)
Recharge shall not be concentrated to one area. It shall be distributed to multiple areas throughout the site.
(d)
The recharge volume criteria does not apply to any portion of a site designated as a stormwater hotspot. Hotspots are defined in the Massachusetts Department of Environmental Protection Volume One: Stormwater Policy Handbook as sites with higher potential pollutant loads, including:
[1]
Auto salvage yards (auto recycler facilities).
[2]
Auto fueling facilities (gas stations).
[3]
Fleet storage areas (cars, buses, trucks, public works).
[4]
Vehicle service and maintenance areas.
[5]
Vehicle and equipment cleaning facilities.
[6]
Commercial parking lots with average trip generation rates of 1,000 or greater per day, such as fast-food restaurants, convenience stores, high-turnover (chain) restaurants, shopping centers, and supermarkets.
[7]
Road salt storage and loading areas (if exposed to rainfall).
[8]
Commercial nurseries.
[9]
Flat metal (galvanized metal or copper) rooftops of industrial facilities.
[10]
Outdoor storage and loading/unloading areas of hazardous substances.
[11]
SARA 312 generators (if materials or containers are exposed to rainfall).
[12]
Marinas (service, repainting, and hull maintenance areas).
B.
Pretreatment.
(1)
To prevent premature failure, the design of stormwater treatment devices shall include a pretreatment device or method that will trap sand and sediments to avoid clogging the treatment mechanism. Infiltration of stormwater from the treatment device into underlying soils and eventually groundwater aquifers is an important beneficial component of the device. Pretreatment basins must be designed and located to be easily inspected and accessible to facilitate maintenance. Pretreatment devices must also be sized to accommodate a minimum of one year's worth of sediment and debris.
(2)
The following standards shall be followed to ensure that the device will permit sufficient treatment to treat stormwater and allow for a reasonable required maintenance frequency for the best management practice (BMP):
(a)
Pretreatment devices shall be provided for each structural BMP; and
(b)
Pretreatment devices for bioretention areas should include a grass buffer or transition zone between pavement and bioretention (e.g., crushed stone entrance, cobbles) that allows sediment to drop out before entering the treatment device; and
(c)
Pretreatment devices shall be designed to capture anticipated pollutants, such as oil and grease; and
(d)
Pretreatment devices shall be designed and located to be easily accessible to facilitate inspection and maintenance; and
(e)
The Revised Universal Soil Loss Equation (RUSLE) (Note: developed by the Natural Resources Conservation Service, USDA to predict soil erosion to due water) shall be used to calculate sediment deposits that would occur from pervious areas adjacent to the BMP; and
(f)
Pretreatment structures shall be sized to hold an annual sediment loading. An annual sediment load shall be calculated using a sand application rate of 500 pounds/acre for sanding of roadways, parking areas and access drives within the subcatchment area, a sand density of 90 pounds per cubic foot and assuming a minimum frequency of 10 sandings per year. To obtain an annual sediment volume, perform the following calculation:
Area to be sanded (acres) x 500 pounds/Acre-storm ÷ 90 pounds/ft3 x 10 storms/year = cubic feet of sediment/year |
(g)
The developer shall maintain any BMPs used to trap sediment during construction to prevent sediment from leaving the site, and shall remove all sediment from all BMPs when construction is finished and the site is stabilized.
C.
Flooding protection. The following standards should be followed to control peak discharge rates and improve the overall effectiveness of the BMPs. These are minimum design standards.
(1)
The post-development peak discharge rate shall be equal to or less than the pre-development (e.g., forested) peak discharge rate (based on a two-year and ten-year, twenty-four-hour storm); and
(2)
The post-development peak discharge rate shall be equal to or less than the existing development peak discharge rate based on a one-hundred-year, twenty-four-hour storm;
(3)
The site shall be designed to ensure that all runoff from the site up to the one-hundred-year storm enters the control structure. For example, the drainage system may only be sized to handle a ten-year storm, with larger storms flooding the distribution system and traveling overland. This overland flow, or overflow, must be directed into the peak control structure; and
(4)
The applicant shall account for all run-on and run-off (including off-site impacts) in both pre- and post-development conditions; and
(5)
The applicant shall prepare hydrographs for pre- and post-development conditions; and
(6)
The pre-developed condition shall be a forested land cover in good condition; and
(7)
Use TR-55 to develop hydrographs and peak flow rates for the proposed development site. Make sure all areas are accounted for in the pre-/post-runoff calculations. The total tributary area that contributes flow from the proposed site, including runoff entering the site through piped drainage or surface runoff from off-site sources, must be included even if a portion does not contribute flow to the BMP. The objective is for the development's storm drain design to account for total runoff leaving the site; and
(8)
The length of overland sheet flow used in tc calculations shall be limited to no more than 100 feet for pre- and post-development conditions; and
(9)
Use naturalized basins over typical detention basins for peak control. Naturalized basins are attractively landscaped basins that fit better into a natural landscape, with naturally landscaped areas at the ground surface. Naturalized planting themes incorporate native plants and use an informal pattern to mimic the natural environment; and
(10)
Basins shall be easily accessible for maintenance.
D.
Water quality volume. The water quality volume required to be treated shall be calculated as:
Water Quality Volume (ft3) = Impervious Surfaces (ft2) X 1.0 (inch) / 12 (inches per foot) |
E.
Pollutant removal. Stormwater management systems must be designed to remove 80% of the average annual post-construction load of total suspended solids (TSS).
F.
Erosion control. Land clearing and grading for construction purposes leaves soils susceptible to erosion. If not controlled, eroded soils may reach streams and lakes, filling them in and adding pollutants attached to the soil particles. It is important to have controls in place to prevent and control the erosion of disturbed lands. The following standards shall be met for erosion control:
(1)
Prior to any land disturbance activities commencing on the site, the developer shall physically mark limits of no land disturbance on the site with tape, signs, or orange construction fence, so that workers can see the areas to be protected. The physical markers shall be inspected daily; and
(2)
Appropriate erosion and sediment control measures shall be installed prior to soil disturbance. Measures shall be taken to control erosion within the project area. Sediment in runoff water shall be trapped and retained within the project area. Wetland areas and surface waters shall be protected from sediment; and
(3)
Sediment shall be removed once the volume reaches 1/4 to 1/2 the height of the silt fence or hay bale; and
(4)
Divert off-site runoff from highly erodible soils and steep slopes to stable areas; and
(5)
Land disturbance activities requiring a stormwater management permit under Chapter 198, Stormwater Management — Low-Impact Development, must submit a sequencing plan that requires stormwater controls to be installed and the soil stabilized. A construction phasing plan shall be submitted to the Planning Department prior to any construction on the site. Mass clearings and grading of the entire site shall be avoided; and
(6)
Soil stockpiles must be stabilized or covered at the end of each workday. Stockpile side slopes shall not be greater than 2:1. All stockpiles shall be surrounded by sediment controls; and
(7)
The area of disturbance shall be kept to a minimum. Disturbed areas remaining idle for more than 14 days shall be stabilized; and
(8)
For active construction areas such as borrow or stockpile areas, roadway improvements and areas within 50 feet of a building under construction, a perimeter sediment control system shall be installed and maintained to contain soil; and
(9)
A tracking pad shall be constructed at all entrance/exit points of the site to reduce the amount of soil carried onto roadways and off the site; and
(10)
Dust shall be controlled at the site; and
(11)
On the cut side of roads, ditches shall be stabilized immediately with rock rip-rap or other nonerodible liners or, where appropriate, vegetative measures such as sod; and
(12)
Permanent seeding shall be undertaken in the spring from March through May, and in late summer and early fall from August to October 15. During the peak summer months and in the fall after October 15, when seeding is found to be impractical, an appropriate temporary mulch shall be applied. Permanent seeding may be undertaken during the summer if plans provide for adequate mulching and watering; and
(13)
All slopes steeper than 3:1 (h:v, 33.3%), as well as perimeter dikes, sediment basins or traps, and embankments must, upon completion, be immediately stabilized with sod, seed and anchored straw mulch, or other approved stabilization measures. Areas outside of the perimeter sediment control system must not be disturbed; and
(14)
Monitoring and maintenance of erosion and sediment control measures throughout the course of construction shall be required. The applicant shall submit an Operation and Maintenance Plan for temporary and permanent erosion control measures as part of the application package; and
(15)
Temporary sediment trapping devices must not be removed until permanent stabilization is established in all contributory drainage areas. Similarly, stabilization must be established prior to converting sediment traps/basins into permanent (post-construction) stormwater management facilities. All facilities used as temporary measures shall be cleaned prior to being put into final operation; and
(16)
All temporary erosion and sediment control measures shall be removed after final site stabilization. Disturbed soil areas resulting from the removal of temporary measures shall be permanently stabilized within 30 days of removal.
G.
Hydrologic and hydraulic criteria for all designs.
(1)
Impervious cover is measured from the site plan and includes any material or structure on or above the ground that prevents water from infiltrating through the underlying soil. Impervious surface is defined to include, without limitation: paved parking lots, sidewalks, rooftops, driveways, patios, and paved, gravel and compacted dirt surfaced roads.
(2)
The specified design storms shall be defined as a twenty-four-hour storm using the rainfall distribution recommended by the United States Department of Agriculture (USDA) Natural Resources Conservation Service (NRCS).
(3)
Proposed residential, commercial, or industrial subdivisions shall apply these stormwater management criteria to the land development as a whole. Individual lots in new subdivisions shall not be considered separate land development projects, but rather the entire subdivision shall be considered a single land development project. Hydrologic parameters shall reflect the ultimate land development and shall be used in all engineering calculations.
H.
Operation and maintenance. A long-term operation and maintenance (O&M) plan must be developed and implemented to ensure that stormwater management systems function as designed. The long-term O&M plan shall include the following:
(1)
Stormwater management system owners;
(2)
Responsible parties for operation and maintenance, including how future property owners will be notified of the presence of the stormwater management system and the requirement for proper operation and maintenance;
(3)
The routine and nonroutine maintenance tasks to be undertaken after construction is complete and a schedule for implementing those tasks;
(4)
Plan that is drawn to scale and shows the location of all stormwater BMPs in each treatment train along with the discharge point;
(5)
Description and delineation of public safety features; and
(6)
Estimated operations and maintenance budget.