[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).
[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.
[Adopted 5-1-2008; amended 2-18-2016]
For the purposes of these guidelines, the following
terms are defined for estimating necessary parking supply within the
Town Center Overlay District:
PUBLIC PARKING SUPPLY DEMAND REDUCTIONS
This involves reducing the overall parking supply cited in
§ 218-23 by assuming that the future public on- and off-street
parking supply created within the Town Center Overlay District will
be shared by Town Center Overlay District land uses and recreational
resources (i.e., the Nashua River Rail Trail) located within a convenient
walking distance of the destinations of parkers.
SHARED PARKING DEMAND REDUCTIONS
This involves reducing overall parking requirements cited
in § 218-23 of the Code of the Town of Groton by creating
an agreement between affected property owners to share available parking
spaces when those spaces are located within a convenient walking distance
of the parker's destination. Such agreements can be applied when land
uses having different parking demand patterns are able to use the
same parking spaces and areas throughout the day and thereby reduce
their combined demands. Shared parking is most effective when sharing
land uses have significantly different peak parking characteristics
that vary by time of day, day of week, and/or season of the year.
In these situations, shared parking strategies will result in fewer
total parking spaces needed when compared to the total number of parking
spaces needed for each individual land use or business. Mixed land
uses tending to benefit from specific shared parking arrangements
include the Nashua River Rail Trail and the mixed uses being considered
for the Town Center Overlay District. This also refers to parking
demands that may be reduced at retail facilities because a proportion
of patrons are expected to walk or bike to the Town Center Overlay
District. For purposes of the Town Center Overlay District, land uses
that may have parking reductions include office, institutional (i.e.,
Town Hall/Fire Department employees and visitors) and certain types
of retail uses (i.e., coffee shops, small retail shops and Nashua
River Rail Trail-oriented retail uses).
SHARED PARKING PLAN
This is a scaled plan (e.g., one inch equals 40 feet) delineating
the parking areas that are to be shared under a shared use agreement.
SHARED USE AGREEMENT
This is a binding legal agreement by and between signatories
representing land uses within the Town Center Overlay District to
share the construction, maintenance, and liability for identified
shared parking facilities within the Town Center Overlay District.
Design of shared parking spaces for regular and accessible spaces shall generally comply with Chapter
218 of the Code of the Town of Groton, § 218-23, Off-street parking and loading. Small-size parking spaces should also be considered by Town Center Overlay District development applicants. Table 14-7 from the ITE Traffic Engineering Handbook (1999) is referenced as a source for small-size parking dimension guidelines that may be employed if some of the parking spaces in the Town Center Overlay District are dedicated for small cars. Such spaces must be clearly signed in the field and shall not include more than 1/3 of the non-public components of the shared parking supply. Compact car spaces shall not be less than eight feet by 16 feet in area versus Groton's standard car spaces that are nine feet by 18 feet in area. For example, a minimum twenty-four-foot aisle for two-way traffic is necessary to accommodate emergency vehicle circulation and backing maneuvers, even for compact car areas. Therefore, an entire parking bay, i.e., a row of only compact cars at 90º parking from on the left and the right, can be a minimum of 54 feet wide versus 60 feet for a similar full-size parking bay. Alternating full size with small car rows can preserve green space. On-street parking, parallel or angle configurations, shall be permitted and encouraged where its design will not present a hazard to pedestrians, block visibility from exiting driveways, or be detrimental to emergency egress from the Fire Department. Sidewalk curb extensions will be considered in areas where motorist visibility of traffic would otherwise be impaired by vehicles parked in close proximity to parked driveways.