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Local Examples: Shared Parking

Local Example – Marlborough, MA: Shared Parking

City of Marlborough Zoning By-Law, §200-25 Off-Street Parking.

B. Application of Parking Requirements.

(3) [amended 4-23-90 by Ord. No. 89/90-3111] Common Parking Areas and Mixed Uses. Parking required for two (2) or more buildings or uses may be provided in combined parking facilities where such facilities will continue to be available for the several buildings or uses and provided that the total number of spaces is not less than the sum of the spaces required for each use individually, except that said number of spaces may be reduced by up to one-half (1/2) such sum if it can be demonstrated that the hours or days of peak parking need for the uses are so different that a lower total will provide adequately for all uses served by the facility. The following requirements shall be met:

  1. Evidence of reduced parking needs shall be documented and based on accepted planning and engineering practice satisfactory to the City Planner and Engineer.
  2. If a lower total is approved, no change in any use shall thereafter be permitted without further evidence that the parking will remain adequate in the future, and if said evidence is not satisfactory, then additional parking shall be provided before a change in use is authorized.
  3. Evidence of continued availability of common or shared parking areas shall be provided satisfactory to the City Solicitor and shall be documented and filed with the Site Plan.
  4. The determination of how a combined or multiuse facility shall be broken down into its constituent components shall be made by the Planning Department.
  5. If any reduction in the total number of parking spaces is allowed as a result of this subsection, then one hundred fifty (150) square feet of open space (per parking space reduced) shall be provided in addition to that required by lot coverage provisions of this Chapter.

Local Example – Waltham, MA: Shared Parking

The General Ordinances of the City of Waltham, Massachusetts, v.9, updated 8-2006, Part III. Zoning Code

ARTICLE V. Parking Requirements

Sec.5.2. Off-street parking requirements.

5.22 Footnotes.

c. Notwithstanding any other parking requirements set forth in this chapter for individual land uses, when any land or building is used for two or more distinguishable purposes (i e , joint or mixed use development), the minimum total number of parking spaces required to serve the combination of all uses shall be determined in the following manner

Multiply the minimum parking requirement for each individual use (as set forth in the applicable section of this chapter for each use) by the appropriate percentage (as set forth below in the Parking Credit Schedule Chart) for each of the five designated time periods and then add the resulting sums from each vertical column. The column total having the highest total value is the minimum shared parking space requirement for that combination of land uses.

Parking Credit Schedule Chart
Weekday Weekday Weekday Weekend Weekend
Night

Midnight to 7:00 a.m. (percent)

Day

7:00 a.m. to 5:00 p.m. (percent)

Evening

5:00 p.m. to Midnight (percent)

Day

6:00 a.m. to 6:00 p.m. (percent)

Evening

6:00 p.m. to Midnight (percent)

Residential 100 60 90 80 90
Office/Industrial 5 100 10 10 5
Commercial/Retail 5 80 90 100 70
Hotel 70 70 100 70 100
Restaurant 10 50 100 50 100
Restaurant associated with hotel 10 50 60 50 60
Entertainment/recreation (theaters, bowling allies, cocktail lounges and similar) 10 40 100 80 100
Day-care facilities 5 100 10 20 5
All other 100 100 100 100 100

Local Example – Stoneham, MA: Flexible Requirements and Shared Parking

Town of Stoneham Zoning Bylaws, 6.0 GENERAL PROVISIONS AFFECTING ALL DISTRICTS

6.3 Off-Street Parking Requirements:

6.3.8 SPECIAL PERMITS FOR PARKING

6.3.8.1 Special permit for a change in parking space requirements: the number of off street parking spaces required by section 6.3.3, of this by law for a use or uses in the Central Business District and in the Commercial I District for Banquet Facilities, Function Halls and Dinner Theaters may be changed by Special permit in accordance with the following provisions:

(1) Special permit criteria: The Planning Board, by special permit, may allow remote parking lots, or shared parking lots which it deems reasonable, based on the following criteria, and other applicable provisions presented in this subsection:

  1. The capacity, location and current level of use of existing parking facilities, both public and private;
  2. The efficient and maximum use in terms of parking needs and services provided;
  3. The relief of traffic and parking congestion;
  4. The safety of pedestrians;
  5. The provision of reasonable access either by walking distance or shuttle vehicle arrangements;
  6. The maintenance of the character of the area.

(2) The following are allowed by Special Permit:

  1. The substitution of parking spaces within municipal parking lots in lieu of or in reduction to the parking requirements of this section, provided they are located within 1600 feet of the building which is intended to be served.
  2. A reduction in parking space requirements: The number of off-street parking spaces required by Section 6.3.3 of this bylaw for a use or uses in the non-residential districts may be reduced by special permit in accordance with the following provisions:

(1) Shared parking: Shared private parking facilities for different buildings or uses may be allowed by Special Permit, subject to the following provisions:

  1. Up to fifty percent (50%) of the parking spaces serving a building may be used jointly for other uses not normally open, used or operated during similar hours. The applicant must show that the peak parking demand and principal operating hours for each use are suitable for a common parking facility.
  2. A written agreement defining the joint use acceptable to the Planning Board of the common parking facility shall be executed by all parties concerned and approved by the Planning Board as part of the special permit process. Such agreement shall be recorded at the Middlesex Registry of Deeds.
  3. Any subsequent change in land uses for which the shared parking proposal was approved, and which results in the need for additional parking spaces, shall require a new special permit application under this subsection.

(2) Remote parking: Remote (satellite) parking areas may be authorized by the Planning Board by special permit, subject to the following provisions:

  1. The satellite parking spaces will be used solely by the employees and, where practicable, clientele of the commercial use;
  2. The off-site parking spaces shall be located to adequately serve the proposed use and shall be within six hundred (600) feet of the building served for clientele of the commercial use. Off-site parking for employees of the business may be located within a distance of one thousand two hundred (1,200) feet, unless shuttle vehicle arrangements are provided as a condition of the special permit. The parking distance shall be measured by the shortest route of pedestrian access, entrance to entrance.

(3) Pedestrian access: Any proposals submitted, which, in the opinion of the Planning Board, provide direct and vital pedestrian access to other abutting commercial properties and serve to improve pedestrian accessibility may reduce the number of parking spaces required by fifteen percent (15%). Pedestrian access shall be provided enough improved pathways, stairway access or other physical improvements, and such access shall be clearly marked.

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Example: Shared Parking Calculation

Source: Driving Urban Environments: Smart Growth Parking Best Practices, Maryland Governor’s Office of Smart Growth, page 7.

Shared Parking - Montgomery County, Maryland

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Local Examples: Parking Siting Regulations

Local Example – Beverly, MA: Parking Siting Restrictions

City of Beverly, CHAPTER 29 ZONING ORDINANCE
29-24 PARKING AND LOADING REQUIREMENTS

C. General Provisions

4. No accessory off-street parking space shall be permitted within the required front yard in any District, except that this shall not be construed as applying to parking required for a one or two-family dwelling.

5. No employee parking shall be permitted within the required front yard in any “IR” District. No parking in any “IR” District shall be permitted less than 15 feet from any lot line.

Local Example – Acton, MA: Parking Location Regulations

Town of Acton, Zoning By-Law, SECTION 6. PARKING STANDARDS

6.9 Special Provisions for Parking in the Village, Kelley’s Corner, and Powder Mill Districts

6.9.1 In the EAV [East Acton Village] District, except as otherwise provided herein, no BUILDING or STRUCTURE shall be located on any LOT and no activity shall be conducted upon any LOT unless off- STREET parking is provided in accordance with the following requirements:

6.9.1.1 No off-STREET parking spaces shall be established between the front line of the principal BUILDING and the sideline of a STREET, except as may be provided otherwise in the Design Provisions for the East Acton Village District.

6.9.2 In the NAV [North Acton Village] District, the following special provisions for parking shall apply:

6.9.2.1 No off-STREET parking spaces shall be established between the front line of the principal BUILDING and the sideline of a STREET.

6.9.4 WAV [West Acton Village] and SAV [South Acton Village] Districts – In the WAV and SAV Districts, except as otherwise provided herein, no BUILDING or STRUCTURE shall be located on any LOT and no activity shall be conducted upon any LOT unless off-STREET parking is provided in accordance with the following requirements:

6.9.4.2 No off-STREET parking spaces shall be established between the front line of the principal BUILDING and the sideline of a STREET, except on LOTS having frontage on more than one STREET. On LOTS having FRONTAGE on more than one STREET, the main BUILDING entrance shall face a STREET and parking spaces shall be located on the opposite side of the main BUILDING entrance.

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Local Examples: Compact Car Spaces

Local Examples: Compact Car Spaces

Local Example – Marlborough, MA: Compact Car Spaces

City of Marlborough
Zoning By-Law, §200-25 Off-Street Parking.

C. Location and Layout of Parking Facilities.

(3) [amended 4-23-90 by Ord. No. 89/90-3111] Full-size Parking Dimensions. The minimum dimensions of full-size parking stalls and aisles shall be as indicated in the Table of Parking Dimensions: Full Size Spaces. [See Subsection C(4) below for compact size spaces.] The complete shall dimensions shall be paved and no deduction shall be obtained for bumper overhang.

TABLE OF PARKING DIMENSIONS: FULL SIZE SPACES
Angle of Parking (degrees) Width of Parking Space (feet) Depth of Parking Space (feet) Width of Maneuvering Aisle* – 1-way (feet) Width of Maneuvering Aisle* – 2-way (feet(
61-90 9 18 24 24
46-60 9 18 18 20
45 9 18 15 20
Parallel 9 20 12 20

NOTES: *Aisle widths may be different than driveway widths. For driveway width requirements, see 200-25.1C(1) and D(1).

(4) Compact-size Parking Spaces. [amended 4-23-90 by Ord. No. 89/90-3111]

(a) Applicability. This subsection shall apply only to parking lots primarily used by employees or residents occupying the site in question and shall not apply to parking areas used by the general public and/or having constant turnover, such as shopping centers, unless authorized at Site Plan Approval based upon determination that safety will be adequately protected and that commonly employed engineering and planning standards have been met in full.

(b) Percentages. Up to thirty-three percent (33%) of parking spaces may be designed for use by cars smaller than full size, hereinafter called “compact cars.”

(c) Additional Open Space Required. For any reduction in total parking area obtained as a result of using compact-sized spaces, an equal or greater area of open space shall be provided in addition to the minimum open space required by the lot coverage provisions of the Chapter.

(d) Location. Compact-size parking spaces, unless restricted for use by and located adjacent to a dwelling unit, shall be located in one (1) or more continuous areas and shall not be – intermixed with spaces designed for full size cars.

(e) Identification. Compact-size parking spaces shall be clearly designed by pavement marking and by direction signs in conformance with the Sign Ordinance, Chapter 63, and labeled as “Compact Cars Only.”

(f) Dimensions. The minimum dimensions of compact size parking stalls and aisles shall be as indicated in the Table of Parking Dimensions: Compact Size Spaces. [See Subsection C(3) above for full size spaces.] The complete stall dimension shall be paved and no deduction shall be obtained for bumper overhang.

TABLE OF PARKING DIMENSIONS: COMPACT SIZE SPACES
Angel of Parking (degrees) Width of Parking Space (feet) Depth of Parking Space (feet) Width of Maneuvering Aisle* – 1-way (feet) Width of Maneuvering Aisle* – 2-way (feet)
61 to 90 8 16 22 22
46 to 60 8 16 18 18
45 8 16 15 18
Parallel 8 16 12 18

NOTES: * Aisle widths may be different than driveway widths. For driveway width requirements, see 200-25.1C(1) and D(1).

Local Example – Needham, MA: Compact Car Spaces

The Town of Needham
Zoning By-Law, 5. GENERAL REGULATIONS

5.1 Off-Street Parking Requirements

5.1.3 Parking Plan and Design Requirements

(e) Compact Cars – Off-street parking areas may be designed to allow up to a maximum of 50% of the total number of parking spaces to be used by compact cars. Compact car spaces shall not be less than 8 feet by 16 feet.

(f) Parking Space Size – Each parking space, except for the allowable percentage for compact cars, shall measure at least 9 feet in width and 18.5 feet in length; however, parallel parking spaces shall be at least 22 feet in length. The required parking space dimensions, including those for compact car spaces, shall not be reduced by obstructions, including, but not limited to, light poles and columns.

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Local Examples: Landscaping Requirements

Local Example – Acton, MA: Landscaping Requirements

Town of Acton
Zoning By-Law, SECTION 6. PARKING STANDARDS

6.7 Parking Lot Design Requirements

All parking lots shall be designed in compliance with the following design standards, except as provided in Section 6.9. In addition, the following standards shall not apply to parking lots serving a single to four-FAMILY residential USE, an Assisted Living Residence with 10 or less residents, a religious USE, and to parking lots with up to 15 parking spaces serving a Conservation USE.

Required parking spaces, loading areas and driveways shall be provided and maintained with suitable grading, paved surfaces and adequate drainage. Any parking lot containing five (5) or more parking spaces shall include landscaping as required below which is, in the opinion of the Special Permit Granting Authority (if the parking area is related to a permitted USE for which a site plan or other special permit is required) or the Building Commissioner (for other parking areas), located and designed to enhance the visual appearance of the parking or loading facility, to ensure traffic safety, and to minimize the adverse effects of the parking or loading facility on the natural environment.

6.7.1 Cells – Parking requirements shall be met by utilization of parking lot cells having a maximum of forty (40) parking spaces per parking lot cell. There shall be a minimum separation distance of thirty (30) feet between parking lot cells.

6.7.2 Set-Backs – Except as may be required elsewhere in this Bylaw, no parking space or other paved surface, other than ACCESS driveways, common driveways or walkways, shall be located within 30 feet of the front LOT line and within 10 feet of the side and rear LOT lines, and notwithstanding the foregoing, no parking space or other paved surface; other than ACCESS driveways, common driveways or walkways; shall be located within the limits of a landscaped buffer area required under Section 10.4.3.5. and Section 10.4.3.6.

6.7.3 ACCESS Driveways – Each LOT may have one ACCESS driveway through its FRONTAGE which shall be 24 feet wide, unless, in the opinion of the Special Permit Granting Authority (if the parking area is related to a permitted USE for which a site plan or other special permit is required) or the Building Commissioner (for other parking areas), a wider and/or greater number of ACCESS driveways is necessary to provide adequate area for safe vehicular turning movements and circulation. An ACCESS driveway for one-way traffic only may be a minimum of 14 feet wide. There shall be no more than one additional ACCESS driveway for each 200 feet of FRONTAGE and all such additional ACCESS driveway(s) shall be at least 200 feet apart on the LOT measured from the centerline of each ACCESS driveway. No driveway for a nonresidential PRINCIPAL USE shall cross land in a residential zoning district in which the PRINCIPAL USE is not allowed.

6.7.4 Interior Driveways – Interior driveways shall be at least 20 feet wide for two-way traffic and 14 feet for one-way traffic.Example image for parking lot design requirements

6.7.5 Notwithstanding the requirements for ACCESS driveways and interior driveways set forth above, ACCESS and interior driveways in the Village Residential District shall be at least 12 feet wide.

6.7.6 Perimeter Landscaping Requirements – All parking lots/cells with more than five (5) spaces and all loading areas shall be bordered on all sides with a minimum of a ten (10) foot wide buffer strip on which shall be located and maintained appropriate landscaping of suitable type, density and height to effectively screen the parking area. The perimeter landscaping requirements shall be in addition to any minimum OPEN SPACE or landscaped buffer area required elsewhere in this Bylaw. However, where the minimum required front, side or rear yard is less than forty (40) feet, the landscaped buffer areas required in Section 10.4.3.6 and the areas required for perimeter landscaping may overlap. In such instances, the landscaping requirements of Sections 10.4.3.6 and 6.7.8 shall be applied in a manner that will, in the opinion of the Special Permit Granting Authority (if the parking area is related to a permitted USE for which a site plan or other special permit is required) or the Building Commissioner (for other parking areas), provide a landscaped buffer as effective as it would be achieved through the separate implementation of the requirements of Sections 10.4.3.6 and 6.7.8.

6.7.7 Interior Area Landscaping Requirements – A minimum of ten percent (10%) of the interior area, exclusive of perimeter landscaping, of a parking lot cell containing more than twenty-five (25) parking spaces must be planted as landscaped island areas. The landscaped islands shall be so located that some portion of every parking space is not more than forty-five (45) feet from either a landscaped island or the perimeter planting area. Landscaped islands shall be dimensioned so that a circle with a minimum radius of 5 feet can be placed at each location within the island except that within the immediate vicinity of driveway or maneuvering aisle roundings and intersections the radius may be reduced to two feet. Curbing, at least five (5) inches in height, shall surround each landscaped island as protection from vehicles. The interior area landscaping requirements shall be in addition to any minimum OPEN SPACE required elsewhere in this Bylaw.

6.7.8 Plantings for Perimeter and Interior Area Landscaping Requirements Shall Consist of

6.7.8.1 At least one shrub per thirty (30) square feet and one shade tree per two hundred (200) square feet of landscaped area shall be provided, unless the Special Permit Granting Authority (if the parking area is related to a permitted USE for which a site plan or other special permit is required) or the Building Commissioner (for other parking areas) or their designee, determine that there exists sufficient existing vegetation to allow for a different amount of new landscaping.

6.7.8.2 Shade trees shall be of a species tolerant to the climatic conditions of Acton and of parking area conditions, and be at least one and three-quarter (1 3/4) inch caliper (measured four feet above grade level).

6.7.8.3 Shrubs shall be a mix of deciduous and evergreen varieties, tolerant to the climatic conditions of Acton, and be at least eighteen (18) inches in height at time of planting. Snow storage areas shall be planted with shrubs that are tolerant to weight and extended duration of snow cover.

6.7.8.4 The remainder of the landscaped areas shall be planted with ground surface cover, such as lawn grass or live ground cover, over at least four (4) inches of topsoil, unless the Special Permit Granting Authority (if the parking area is related to a permitted USE for which a site plan or other special permit is required) or the Building Commissioner (for other parking areas) or their designee, determine that another type of ground surface cover is appropriate for a specific purpose or location.

6.7.8.5 Wherever possible, the above requirements shall be met by retention of existing vegetation.

6.7.8.6 Planting shall be done in accordance with proper landscaping practices.

6.7.8.7 Trees, shrubs, grass and ground cover which die or become diseased shall be replaced.

6.7.8.8 Final locations of all plantings shall be inspected and approved by the Special Permit Granting Authority (if the parking area is related to a permitted USE for which a site plan or other special permit is required) or the Building Commissioner (for other parking areas) or their designee, including the viability of existing vegetation retained after development and any necessary replacements thereof.

6.9 Special Provisions for Parking in the Village, Kelley’s Corner, and Powder Mill Districts

6.9.1.7 The parking lot design requirements of Section 6.7 shall apply in the EAV [East Acton Village] District, except that:

a) The requirements for parking lot cells and separation of cells (Section 6.7.1) shall not apply.

b) The requirements for set-backs (Section 6.7.2) shall not apply. This does not waive the requirements for perimeter landscaping (Section 6.7.6).

c) The interior area landscaping (Section 6.7.7) may be substituted with one or more consolidated bioretention areas with minimum side dimensions measuring at least 38 X 12 feet each. Bioretention areas shall be designed and landscaped to trap and mitigate runoff from paved surfaces consistent with the description and intent of EPA Storm Water Technology Fact Sheet – Bioretention (EPA 832-F-99-012, September 1999), or equivalent. The landscaping requirements of Sections 6.7.8.1 through 6.7.8.5 shall not apply to bioretention areas. Bioretention areas may be sited anywhere in the parking lot that is convenient to manage parking lot traffic and facilitate pedestrian use, including adjacent to and connecting with vegetated areas on the perimeter of a parking lot. Bioretention areas shall be considered part of the minimum required OPEN SPACE.

Local Example – Littleton, MA: Low Impact Development

Town of Littleton
By-Laws, CHAPTER 173 ZONING

ARTICLE VII Parking and Loading Requirements

Section 173-32. Parking requirements.

C. Parking area design.

No off-street parking area shall be maintained within ten (10) feet of a street line. Required parking areas shall be paved and have bumper or wheel guards where needed unless serving a single-family residence or unless, in performing site plan review (see Section 173-16), the Planning Board determines that, because of seasonal or otherwise limited use, an alternative surface will adequately prevent dust, erosion, water accumulation or unsightly conditions. For parking areas of eight (8) cars or more, the following shall apply:

(5) Parking areas for eight (8) or more vehicles shall be drained through catch basins equipped with oil and grease traps and sediment traps unless the topography of the site prevents their use. [Added 5-9-1988 ATM, Art. 14]

(6) To reduce stormwater discharge and improve the attenuation of pollutants, applicants are required to use stormwater control Best Management Practices (BMPs) and Low Impact Development (LID) techniques in parking lot design (i.e., interior landscaping, vegetated/grassy swales, infiltration planters, permeable pavement, rain gardens, etc.).

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LID Frequently Asked Questions

What is Low Impact Development?

Low Impact Development is a way to protect the environment and reduce construction costs at the same time. Conventional design and construction methods generally use expensive systems of curbs, gutters, pipes, and ponds to collect and treat runoff. In contrast, the Low Impact Development approach uses a more decentralized approach; the idea is to reduce the amount of runoff and treat it closer to the source using smaller, less expensive techniques. Basic design strategies seek to reduce the extent of rooftops and paved areas, use infiltration techniques such as bioretention areas and grass swales, and design the site to protect natural features that improve water quality. Some important techniques are listed below. Click on the links to access a fact sheet about each technique.

Does it take up a lot of land?

In many cases, Low Impact Development techniques can reduce the amount of land devoted to stormwater management, because smaller detention ponds are necessary. Green roofs take up no extra space at all, and techniques such as bioretention areas, grass filter strips, and swales can also help to fulfill site landscaping/open space requirements. Narrower roadways and smaller parking lots actually conserve land.

What about standing water where mosquitoes can breed?

All Low Impact Development techniques are designed to prevent standing water and pest problems. Bioretention areas should drain within 72 hours after a rainstorm, and should be designed with an overflow outlet to prevent flooding. On sites with tight soils, bioretention and infiltration areas can be designed with perforated underdrains to allow rapid drainage. Cisterns and rain barrels should all be fitted with screens to prevent mosquito breeding.

Won’t narrower roadways impede fire trucks and ambulances?

Narrow streets in low-traffic residential areas are generally not a problem for emergency access, especially since on-street parking is rare (most new homes have off-street parking.) Conventional street widths are based on a scenario in which two fire trucks going in opposite directions need to pass each other at full speed with cars parked on both sides of the street. Alternative roadway cross-sections can provide sufficient room for passage of emergency vehicles, with the recognition that oncoming traffic may need to pull into a parking lane. According to the Center for Watershed Protection, the U.S. Fire Administration and the Massachusetts State Fire Marshal approves of street widths as narrow as 18 feet.

Won’t flooding be a problem without curbs and gutters?

Properly designed Low Impact Development techniques will convey water away from buildings and paved areas as quickly as conventional stormwater systems. Because LID emphasizes infiltration and reduction of impervious surfaces, there will actually be less runoff and a lower potential for flooding downstream. With a decentralized approach, one component (such as one bioretention cell) might fail without compromising the integrity of the entire system.

Does Low Impact Development cost more than a conventional approach?

Some Low Impact Development techniques can cost more than conventional approaches, but overall LID is cost-competitive because it can reduce the size of stormwater pipes and downstream ponds, reduce the amount spent on paving, enhance site aesthetics and value. The life-cycle cost of green roofs is lower than conventional roofs due to a much longer life span and considerable savings on heating and cooling costs.

Does Low Impact Development involve expensive and complicated maintenance?

All stormwater management structures require some sort of ongoing maintenance, and LID techniques are no different. However, many of the maintenance activities associated with LID strategies are quite simple and can be conducted by property owners or landscaping crews, with proper direction. Examples include mulching bioretention areas, reseeding or revegetating swales and rain gardens, picking up trash, removing accumulated sediment and dead vegetation, and monitoring performance of the system. Rarely, more complex maintenance is necessary and will involve professionals and heavy equipment; excavation and rehabilitation of bioretention areas or infiltration trenches is one such activity.

Do these techniques work in cold climates?

In Massachusetts, all stormwater management systems need to be designed to account for freezing conditions, snow plowing, and runoff from springtime snow melt. LID techniques should be selected accordingly, with design modifications (such as those outlined in the publication Stormwater BMP Design Supplement for Cold Climates) to improve performance during the winter months. Many techniques such as bioretention areas, filter strips, and swales can be used as snow storage areas during the winter months, and low-impact site and roadway design can reduce the volume of snow that needs to be plowed. Adequate setbacks and design standards will reduce the risk of frost heave.

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Fact Sheet: Roadways and Parking Lot Design

One of the simplest ways to cut down on stormwater runoff is to reduce the amount of impervious cover associated with roadways and parking lots. Careful design is the key to reducing pavement while still providing good site access and adequate parking. Good road and parking lot design can also create opportunities for decentralized stormwater management in bioretention areas, roadside swales, and infiltration structures. Basic strategies for roadway design include low-impact roadway layouts, narrow road widths, shared driveways, and open-section roadways. Parking lots designers should look at strategies to break up large parking lots, maximize shared parking, rethink parking requirements, and use permeable paving where appropriate.

Low-impact roadways use a narrower, more traditional design that enhances neighborhood character. Less runoff is created and it is directed to roadside swales for treatment and conveyance.

Design Objectives

  • Reduce total impervious surface.
  • Reduce road/parking construction costs.
  • Provide safe access and adequate parking.
  • Minimize disturbance to natural site hydrology.
  • Create opportunities for stormwater treatment and infiltration.
  • Improve site appearance.

Alternative road and parking designs may offer cost savings for developers, because there is less pavement to construct and less stormwater runoff to treat. In some cases, more compact parking may allow higher site densities. The primary impediment to these strategies may be resistance at the permitting stage. Many communities stringently enforce elaborate and often excessive roadway and parking standards in an effort to prevent development. Developers, advocates, and regulators who understand the benefits of Low Impact Development need to work together to point out that alternative designs can provide safe access and sufficient parking, as well as environmental and aesthetic benefits.

Applications and Design Principles

Roadway width

Excessively wide streets are the greatest source of impervious cover (and stormwater runoff) in most residential developments. Some local codes require streets up to 40 feet wide in subdivisions with only a dozen houses. These inappropriate standards result from blanket application of high volume/high speed road design criteria, overestimates of on-street parking demand, and the perception that wide streets result in faster emergency response times.

Narrower road sections and alternative road profiles can reduce stormwater runoff and mitigate its impacts, while still allowing safe travel, emergency vehicle access, and adequate parking. For most low-traffic roads, a 24’ road width is sufficient to accommodate two way traffic, and even narrower widths should be used in very low traffic conditions (e.g., a six-lot subdivision.) The National Fire Protection Administration Uniform Fire Code (2003) recommends a minimum unobstructed width of just 20 feet, with the recognition that local authorities set lower standards if turnouts or alternate exits are available.

Recommended Minimum Street Widths
Width (feet) Source
 20 National Fire Protection Administration
18 (minimum) Massachusetts State Fire Marshall
22 American Association of State Highway and Transportation Officials
24 (on-street parking)
16 (no on-street parking)
Baltimore County, Maryland
20 Prince George’s County, Maryland
18 (one lane of parking)
26 (parking both sides)
Portland, Oregon

Source: Center for Watershed Protection

In order to achieve the environmental benefits of narrower street widths, regulators must make clear that they are willing to adjust site design standards to provide developers with the opportunity to try alternative designs. One preliminary step is to require parking on one side of the street only. This is appropriate where most houses have off–street parking. Design standards can also allow parking lanes or road shoulders made of permeable paving, such as grass pavers or paving blocks.

Some communities are moving to roadways that us a single travel lane and one or two “queuing lanes,” which can be used for either parking or travel. This strategy can reduce street width by a third, and it does not affect travel except when two cars need to pass each other at the spot where a third car is parked, in which case one car pulls into the queuing lane until the oncoming car has passed. Research indicates that “tight streets” actually improve traffic safety by encouraging vehicles to slow down in residential neighborhoods. Throughout Massachusetts, many older neighborhoods built before current standards were enacted have narrow streets that function well, tame traffic, and lend character to the community.

Roadway Profile

Curbs and gutters concentrate stormwater runoff and increase its velocity, impeding decentralized treatment and infiltration. LID strategies recommend open-section roadways flanked by filter strips and swales instead of curbs and gutters. These LID techniques, built on the model of “country drainage,” help to filter roadway runoff, promote infiltration, and reduce runoff velocity, resulting in lower peak discharge rates. If properly designed, open section roadways will be no more prone to flooding than conventional roadway profiles. If curbs are deemed necessary to stabilize the roadway edge, the design can use invisible curbs (same level as the road surface), periodic curb cuts, or perforated curbs to allow stormwater to run off the roadway edge.

A schematic diagram of an open-section roadway, with permeable paving parking lanes and roadside swales. Swales should be located between the roadway and a sidewalk, where present.

Schematic of an open-section roadway

A schematic diagram of an open-section roadway, with permeable paving parking lanes and roadside swales. Swales should be located between the roadway and a sidewalk, where present. Image: Valley Branch (MN) Watershed District

Roadway layout

The location and layout of roadways can also be modified to improve post-development hydrology. Roadways should be placed to avoid crossing steep slopes where significant cut and fill will be required. They should run parallel to contours on gentle slopes and perpendicular to contours on steeper slopes. Design of a roadway network may involve some give and take between reducing total roadway length and road layouts compatible with existing topography. On low-speed streets, clearing and grading should be limited to a small strip of land (5’) on either side of the roadway and sidewalk.

In residential subdivisions, shared driveways can reduce site development costs as well as impervious surface coverage. Property owners will also realize some savings through shared snow plowing costs. Driveways can be limited to 9 feet in width. They should be sloped or crowned so that they drain evenly onto adjacent vegetated areas (not onto the street) where the runoff will infiltrate or travel via sheetflow.

Turnarounds and Cul-de-Sacs

Many residential streets end in large cul-de-sacs up to 80 feet across, which generate large amounts of runoff during storms. Alternative designs can reduce runoff and improve neighborhood character, while still providing sufficient room for fire trucks and school buses to maneuver. One simple approach (applicable to both new construction and retrofits) is to create a landscaped island in the middle of a standard-size cul-de-sac. A 30-foot island in an 80-foot diameter cul-de-sac will reduce the impervious surface by 15%; if the island is designed and built as a bioretention area, and the roadway graded appropriately, this strategy can also treat roadway runoff.

A 20-foot diameter landscaped island in a cul-de-sac can reduce impervious surface by 25%. Cul-de-sac islands can also be designed to treat and infiltrate runoff through bioretention. Image: Valley Branch (MN) Watershed District

Other design changes can produce even greater benefits. Reducing the radius of a cul-de-sac from 40 feet to 30 feet yields a 45% reduction in paved surface (5,000 sq. ft versus 2,800 sq. ft.) A T-shaped hammerhead occupies even less space but still provides sufficient room for turning vehicles and fire trucks (though it may require a 3-point turn.) Depending on the length of the street, designers should consider a one-way loop road with parking on one side. Cul-de-sac design is definitely one area where regulatory standards prevent creative designs; regulators should consider re-wording their regulations to replace geometric standards with performance standards.

Parking Lots

Expansive parking lots that drain to just a few catch basins create large volumes and high velocities that require the use of pipe-and-pond stormwater techniques. The LID approach encourages designers to create multiple smaller parking lots separated by natural vegetation and bioretention areas. On hilly sites, the creation of multiple parking areas at different elevations can reduce the amount of grading necessary and preserve natural hydrology.

Permeable paving is rarely appropriate for use in high traffic parking lots, but some success has been found with hybrid parking lots, which use conventional paving for driveways and aisles, and permeable paving for stalls. Permeable paving may also be appropriate for overflow parking areas, which are generally used only a few weeks out of the year.

A schematic drawing of a parking lot that uses a variety of low impact techniques. Parking areas are separated by vegetated swales that convey runoff to bioretention areas, and permeable paving is used for overflow parking at the periphery of the lot. A bike rack and transit stop help to reduce the number of auto trips to the site. Image: Robert W. Droll, ASLA

Other strategies include reducing the total number of parking spaces and reducing the size of some parking spaces. Many communities have provisions for shared parking, so that mixed use developments, or single-use developments near other uses, can share parking according to a formula based on the peak demand periods; residents use the parking spaces at night and customers or employees use the same spaces during the day. Parking spaces designed for compact cars can also help to limit impervious coverage.

Considering the aesthetic and environmental impacts of large parking areas, community boards might consider parking maximums, as well as parking minimums, in order to prevent oversized parking lots and ensure that supply is in line with demand.

Benefits and Effectiveness:

  • Narrower roadways, smaller parking areas, and smaller stormwater management systems result in lower site development costs.
  • A hierarchy of streets sized according to daily needs yields a wide variety of benefits: lower average speeds, more room for trees and landscaping, improved aesthetics, and reduced heat island effect.
  • Designs that reduce the amount of parking and break it up into multiple smaller lots separated by vegetation create more attractive developments.

Limitations:

  • Alternative roadway and parking designs may conflict with local codes, which often have strict requirements for road widths and drainage systems. However, many boards may be willing to adjust their standards if developers, advocates, and neighbors support the alternative design.
  • Emergency service access is a common concern with reduced street widths. Where possible, these concerns can be addressed through education or multiple points of access to a site.

Cost:

Narrower streets and smaller parking lots cost less than conventional streets because less grading, base material, and pavement is required. Open section roadways cost considerably less than standard designs due to the elimination of curbs and gutters.

Additional References:

  • A Policy on Geometric Design of Highways and Streets, 5th Edition; American Association of State Highway and Transportation Officials, 2004
  • Shared Parking Guidelines; Institute of Transportation Engineers, Washington DC; 1995.
  • The American Planning Association has published a variety of reports on parking standards, as part of its Planners Advisory Service.

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Fact Sheet: Green Roofs

A green roof is a low-maintenance vegetated roof system that stores rainwater in a lightweight engineered soil medium, where the water is taken up by plants and transpired into the air. As a result, much less water runs off the roof, as compared to conventional rooftops. Green roofs have been in use in Europe for more than 30 years; they are easy to incorporate into new construction, and can even be used on many existing buildings.

Green roofs provide an extra layer of insulation that reduces heating and cooling costs, and they are likely to last much longer than conventional roofs, since the roofing material itself is shielded from ultraviolet light and thermal stress. The vegetation on green roofs also improves air quality, enhances the appearance of the building, and reduces the urban “heat island” effect.

Management Objectives

  • Reduce total runoff volume through rainwater storage and evapotranspiration.
  • Reduce peak discharge rates.
  • Reduce heating and cooling costs through roof insulation.
  • Extend roof life.
  • Improve building appearance.
  • Reduce “heat island” effect and improve local air quality.

There are two distinct types of green roofs: extensive green roofs require less than 6” of soil medium and support mostly herbaceous plants; these utilitarian “roof meadows” generally have no public access and require little maintenance. In contrast, intensive green roofs include shrubs and small trees planted in more than six inches of growing medium; they are often designed as accessible building amenities. This fact sheet focuses on extensive green roofs and their stormwater management benefits. Both types of green roofs seek to transform rooftops from “wasted space” into a form of infrastructure that has environmental, economic, aesthetic, and social benefits.

Applications and Design Principles

Green roofs are appropriate for commercial, industrial, and residential structures, especially those with a wide roof area. They can be incorporated into new construction or added to existing buildings during renovation or re-roofing. Most green roofs are built on flat or low-angle rooftops, but some have been installed on pitched roofs up to 40% slope, with special design features to prevent slumping and ensure plant survival.

Bruker Electronics' Green Roof

A photo of the green roof at the Bruker Deltronics Headquarters in Billerica, MA. Photo: © 2005, Roofscapes, Inc. Used by permission; all rights reserved.

Green roofs are appropriate anywhere it is desirable to reduce the overall amount of stormwater runoff. They are an excellent technique to use in dense urban areas, in areas where infiltration is difficult due to tight soils or shallow bedrock, or on sites where infiltration is undesirable due to existing soil contamination. Because green roofs return rainwater to the atmosphere, they should not be used in situations where groundwater recharge is a priority, such as in stressed basins with chronic low-flow conditions. In these circumstances, roof runoff should be infiltrated whenever feasible.

Schematic Diagram of Green Roof System

A schematic diagram of a green roof system. Image: City of Portland, OR Environmental Services.

Like conventional roofs, the basic element of a green roof is a waterproof membrane over the roof sheathing. The system also includes a root barrier; a drainage layer; filter fabric; and 2”-6” of a lightweight growth substrate consisting of inorganic absorbent material such as perlite, clay shale, pumice, or crushed terracotta, with no more than 5% organic content. Substrates should not be too rich in organic material such as compost, because of the potential for settling, nutrient export, and too-rapid plant growth. Gravel ballast is sometimes placed along the perimeter of the roof and at air vents and other vertical elements, in order to promote drainage and facilitate access.

Extensive green roofs require moderate structural support which can be easily accommodated during design for new construction; existing roofs may be adequate or may require additional structural supports that can be added during re-roofing or renovation. An extensive green roof may weigh approximately 10-25 pounds per square foot when fully saturated, whereas a conventional rock ballast roof weighs approximately 10-12 pounds per square foot (neither figure includes potential snow load.)

Vegetation on extensive green roofs usually consists of hardy, low-growing, drought-resistant, fire-resistant plants that provide dense cover and are able to withstand heat, cold, and high winds. Varieties commonly used include succulents such as sedum (stonecrop) and delosperma (ice plant.) During dry periods, these plants droop but do not die back; when it rains, they quickly revive and absorb large amounts of water. Grasses and herbs are less common on green roofs because to survive dry periods they require either irrigation or deeper substrate that retains more water.

A common concern about green roofs is the potential for leaks. The performance of green roofs has improved dramatically since the 1970s, when many leak problems were associated with the first generation of green roofs. Current waterproofing materials, root barriers, and rigorous design and construction standards have largely eliminated these problems; low-cost electronic grids installed under the membrane during construction can also help to pinpoint leaks and minimize repair costs.

Benefits and Effectiveness:

  • Green roofs effectively reduce stormwater runoff. Researchers at North Carolina State have found that a 3” green roof can retain approximately 0.6” of rain for each rainfall event, even when storms come on consecutive days. The Center for Green Roof Research at Penn State University reports that a 4” green roof can retain 50% of total rainfall over a series of storm events.
  • Green roofs reduce peak discharge rates by retaining runoff and creating longer flow paths. Research indicates that peak flow rates are reduced by 50% to 90% compared to conventional roofs, and peak discharge is delayed by an hour or more.
  • Green roofs lower heating and cooling costs because the trapped air in the underdrain layer and in the root layer help to insulate the roof of the building. During the summer, sunlight drives evaporation and plant growth, instead of heating the roof surface. During the winter, a green roof can reduce heat loss by 25% or more.
  • Because green roofs shield roof membranes from intense heat and direct sunlight, the entire roofing system has a longer lifespan than conventional roofs.
  • The presence of a green roof helps to reduce air temperatures around the building, reducing the “heat island” effect and reducing the production of smog and ozone, which forms in the intense heat (175 degrees) over large conventional roofs. The vegetation on green roofs also consumes carbon dioxide and increases the local levels of oxygen and humidity.
  • Green roofs have demonstrated aesthetic benefits that can increase community acceptance of a high-visibility project; they may also add value to the property if marketed effectively.

Limitations

  • Load restrictions are usually the main limitation for green roofs in retrofit applications. A professional engineer must assess the necessary load reserves and design a roof structure that meets state and local codes.
  • Slopes greater than 15% require a wooden lath grid or other retention system to hold substrate in place until plants form a thick vegetation mat.
  • Green roofs should not be used where groundwater recharge is a priority, such as in aquifer recharge areas or watersheds experiencing low-flow stresses.
  • The initial construction cost is higher than conventional roofs.

Maintenance

  • Green roofs require some support during establishment and then yearly maintenance thereafter. Plants or sprigs should be irrigated until established, and additional plants or sprigs added to ensure good plant coverage if necessary. With drought-resistant vegetation, irrigation of an extensive green roof is rarely necessary after the two-year establishment period.
  • Weeding and mulching may be needed during the establishment period and periodically thereafter over the life of the roof. Any woody plants which become established on the roof need to be removed regularly.
  • If necessary (many roofs can survive on deposition of airborne nitrogen and biomass breakdown), application of a slow-release fertilizer once a year will ensure continued vigorous growth of the vegetation. Soluble nitrogen fertilizers and compost should not be used due to the potential for nutrient and bacteria export.

Cost

Green roofs start at $5 per square foot. They generally cost more to install than conventional roofs, but are financially competitive on a life-cycle basis because of longer life spans (up to 40 years), increased energy efficiency, and reduced stormwater runoff. If the application is a retrofit, structural upgrades may increase the cost somewhat.

Design Details

  • Waterproof membranes are made of various materials, such as modified asphalts (bitumens), synthetic rubber (EPDM), hypolan (CPSE), and reinforced PVC. The most common design used in Europe is 60-80 mil PVC single-ply roof systems. Modified asphalts usually require a root barrier, while EPDM and reinforced PVC generally do not. Attention to seams is critical because some glues and cements are not always root impermeable.
  • The underdrain layer may be constructed of perforated plastic sheets or a thin layer of gravel. Pitched roofs and small flat roofs may not require an underdrain.
  • Vegetation should be low-growing, spreading perennial or self-sowing annuals that are drought tolerant. Appropriate varieties include sedum, delospermum, sempervivium, creeping thyme, allium, phloxes, anntenaria, ameria, and abretia. Vegetation may be planted as vegetation mats, plugs or potted plants, sprigs (cuttings), or seeds. Vegetation mats are the most expensive but achieve immediate full coverage. Potted plants are also expensive and labor intensive to install. Sprigs are often the most cost effective option, even considering that initial irrigation is necessary and repeat installations may be required due to mortality. Conventional sod should not be used because it requires irrigation, mowing, and maintenance.
  • Access routes should be identified during the design phase, and access paths of gravel or other inert materials provided, as well as safety harness hooks for inspection and maintenance personnel.

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Fact Sheet: Grass Filter Strips

Grass filter strips are low-angle vegetated slopes designed to treat sheet flow runoff from adjacent impervious areas. Filter strips (also known as vegetated filter strips and grassed filters) function by slowing runoff velocities, filtering out sediment and other pollutants, and providing some infiltration into underlying soils. Because they use sheet flow and not channelized flow, filter strips are often more effective than swales at removing suspended solids and trash from runoff. They provide good “pretreatment” of stormwater that will then be routed to another technique such as a bioretention area.

A filter strip adjacent to this filling station provides room for snow storage and can remove sediment and organics from runoff. Photo: Steve Haubner, Atlanta Regional Commission

Management Objectives

  • Remove suspended solids, heavy metals, trash, oil and grease.
  • Reduce peak discharge rate and total runoff volume.
  • Provide modest infiltration and recharge.
  • Provide snow storage areas.
  • Improve site landscaping.

Filter strips were originally used as an agricultural treatment practice, but have recently been used in more urban and suburban locations. They differ slightly from buffer strips, which are natural vegetated areas alongside streams and lakes; buffer strips are left undisturbed for habitat protection and visual screening, while filter strips are altered areas designed primarily for stormwater management. Like many other LID techniques, vegetated filter strips can add aesthetic value to development. They cost significantly less than “hardscaped” stormwater infrastructure and also provide a convenient and effective area for snow storage and treatment.

Applications and Design Principles

Filter strips are appropriate for roadside applications and along the edge of small- to medium-sized parking lots, so long as the tributary area extends no more than 60 feet uphill from the buffer strip. They can also be used to treat roof runoff that is discharged over a level spreader. Filter strips are ideal components of the outer zone of a stream buffer, or as pretreatment to another stormwater treatment practice. They are generally require too much land area for applications in urban areas. The contributing drainage area should generally be less than five acres.

Filter strips work best when they are at least 20 feet long (downhill axis), though shorter strips will still provide some treatment. They should have slopes between 1% and 15%, preferably in the lower end of that range. It is critical for filter strips to be planar or convex, since any undulation in the surface or obstructions can cause concentrated flow that leads to erosion, channelization, and loss of water quality benefits.

Grass Filter Strip

Here a filter strip is being used as pretreatment for parking lot runoff directed to an infiltration basin. Note concrete level spreader (at right) to facilitate sheetflow across filter strip. 

The design should seek to keep runoff velocity in the low to moderate range (less than 2 feet per second) in order to maximize water quality benefits. This can be done by limiting the size of the contributing impervious surface. Both the top and toe of the slope should be as flat as possible to encourage sheet flow. A pea gravel or cement level spreader (with a lip) at the top of the filter strip will improve sheet flow and will capture some sediment.

Some filter strips are designed with a pervious berm at the downhill end of the filter strip, to detain water temporarily, increasing infiltration and reducing peak discharge rates. This berm can significantly enhance water quality benefits if it is designed to impound the water quality volume.

Benefits and Effectiveness:

  • Filter strips provide runoff pretreatment by trapping, filtering and infiltrating particulates and associated pollutants. TSS removal rates range from 40%-90%. Effectiveness depends largely on the quantity of water treated, the slope and length of the filter strip, the type of vegetation, and the soil infiltration rate.
  • Vegetated filter strips also reduce runoff velocities and increase the time of concentration as compared to channelized flow, resulting in a reduction of peak discharge rates.
  • Filter strips may provide groundwater recharge as runoff infiltrates into soil; recharge may be considerable if design incorporates a ponding area at the toe of the slope.
  • Filter strips can serve as a location for snow storage during winter months and will also help to trap and treat the salt and sand in snow when it melts.
  • Filter strips are inexpensive to construct, especially when compared to conventional curb-and-gutter systems.
  • Vegetated filter strips help to accent the natural landscape by providing green space adjacent to parking lots and roadways.

Limitations

  • Because filter strips infiltrate runoff to groundwater, they could be inappropriate at stormwater “hotspots” (such as gas stations) with higher potential pollutant loads. They should be combined with other BMPs to ensure adequate treatment of polluted runoff prior to discharge.
  • Channelization and premature failure may result from poor design, imprecise construction, or lack of maintenance. Proper design requires a great deal of finesse, and slight problems in the construction, such as improper grading, can render the practice less effective in terms of pollutant removal.
  • Filter strips have low removal rates for nutrients, so they must be used in conjunction with other best management practices.
  • Filter strips often require lots of space, making them often infeasible in urban environments where land prices are high.

Maintenance

  • Inspect level spreader monthly and remove built-up sediment.
  • Inspect vegetation monthly for rills and gullies and correct. Fill any depressions or channels. Seed or sod bare areas.
  • In the year following construction, inspect the filter strip regularly to ensure that grass has established. If not, replace with an alternative species. Allow natural succession by native grasses and shrubs if it occurs.
  • Mow grass, as rarely as 2-3 times per year, to maintain 4″ to 6” of dense grass cover. Grass clippings should be collected and composted elsewhere. Provide a minimum of fertilizer only when necessary. Mow when the soil is dry and firm to prevent rutting.
  • Semi-annually, remove sediment that has accumulated to prevent berms or channels.

Cost

Filter strips cost considerably less to construct than many hardscaped stormwater management structures such as curbs, storm sewers, and ponds. The primary direct expenses are clearing, grading, and seed or sod. Additional expenses may include construction of a level spreader at the top of the strip or a berm at the toe of the slope.

The most significant cost of filter strips may be an indirect expense, which is the cost of the land, which may be very valuable in dense urban settings. In many cases, however, open spaces and buffers are required by municipal landscaping or zoning regulations, and filter strips may be used to satisfy these requirements. Established vegetated buffers may also add value a property.

Design Details

  • The limiting design factor for filter strips is not total drainage area but rather the length of flow contributing to it. Because sheetflow runoff becomes concentrated flow as distance increases, the contributing area to a vegetated buffer should be no more than 60 feet for impervious surfaces, and 100 feet for pervious surfaces.
  • Slopes should be between 1% and 15%, though slopes less than 5% are preferred. The top and toe of the slope should be as flat as possible.
  • The filter strip should be at least 20′ long (downhill length) to provide water quality treatment. Minimum width is 8’ or 0.2 X length of flow over the impervious surface upstream of the filter strip.
  • Depth of sheetflow should be less than 0.5” for the design storm. Depending on the pollutant removal required, residence time should be at least 5 minutes, preferably 9 minutes or more.
  • Use Manning’s equation to calculate velocity, assuming hydraulic radius equals depth, with n values of 0.20 for mowed grass slope and 0.24 for infrequently mowed grass slope. Normal velocity should be <1.0 feet/second for design flow, with maximum permissible velocity of 3.0 feet/second for peak discharge during 10-year storm.
  • Use a cement level spreader or pea gravel diaphragm at the top of the slope.
  • Filter strips can be designed with a pervious berm of sand and gravel at the toe of the slope. This feature provides an area for shallow ponding at the bottom of the filter strip. Runoff ponds behind the berm and gradually flows through outlet pipes in the berm. The volume ponded behind the berm should be equal to the water quality volume.
  • Designers should choose a grass that can withstand calculated flow velocities, and both wet and dry periods. Also consider depth to groundwater and choose facultative wetland species if appropriate.
  • If filter strip will be used for snow storage, use salt tolerant vegetation (e.g., creeping bentgrass.)
  • During construction, divert runoff from unstabilized areas away from filter strips.
  • Protect the underlying soil from compaction to the extent possible: work from outside the boundaries of the filter strip or use oversized tires and lightweight equipment.
  • Disturbed areas steeper than 4:1 should be protected during establishment with erosion control blankets.

Additional Resources:

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LID Principles and Techniques

Principles of LID

Work with the landscape.

Identify environmentally sensitive areas and important local features, then outline a development envelope that protects those areas. Maintain slopes and flow paths; minimize grading and tree clearing.

Focus on prevention.

Minimize runoff by using narrow roadways, smaller parking areas, and permeable paving on sidewalks and overflow parking areas. Use green rooftops to store and evaporate rainfall before it even leaves the roof.

Micromanage stormwater.

Design the site to create many small sub-watersheds and “micromanage” runoff close to where it is created in small decentralized structures. Use a “treatment train” of multiple techniques to maximize filtration and recharge.

Keep it simple.

Before resorting to expensive piped systems, use low-cost approaches and nonstructural practices, such as rain gardens, street sweeping, and public education. Send clean roof runoff to vegetated areas for infiltration.

Practice multi-tasking.

Create a multifunctional landscape with stormwater management components that provide filtration, treatment, and infiltration. Create features that function as open space, wildlife habitat, and snow storage area, in addition to stormwater treatment.

Maintain and sustain.

Teach homeowners and landscaping professionals how to monitor and maintain rain gardens and swales. Provide public works departments with adequate funding; educate the public to reduce pollution.

Low Impact Development Slide Show

Download the MAPC powerpoint slide show about Low Impact Development, which the outlines six major principles of LID, ten important techniques, and considerations for implementation. We invite you to use it for presentations to local boards, community groups, business associations, and developers. If you have any questions, please email [email protected].

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