STORMWATER RUNOFF QUALITY AND QUANTITY FROM TRADITIONAL AND LOW IMPACT DEVELOPMENT WATERSHEDS
<br />existed before urban development (USEPA, 2000).
<br />The LID concepts utilize various best management
<br />practices (BMPs) such as bioretention, cluster hous-
<br />ing, grassed swales, and public education (Prince
<br />George's County, 1999).
<br />Most studies of stormwater BMPs have focused on
<br />individual treatments, and few have incorporated
<br />more than one BMP into an investigation (Richards
<br />et al., 1981; Urbonas, 1994; Legret and Colandini,
<br />1999; Davis et al., 2001a; Kopp and Guillard, 2002;
<br />Deletic, 2005). Such studies have examined perme-
<br />able pavements (Brattebo and Booth, 2003), educa-
<br />tion (Dietz and Clausen, 2004), and vegetative swales
<br />(Rushton, 2001).
<br />There are even fewer studies on LID designs, and
<br />these have relied mostly on assumptions about their
<br />effectiveness for stormwater management. For exam-
<br />ple, a survey of local governments in several states
<br />concluded that planned greenfield developments,
<br />which utilized LID methods, surpassed traditional
<br />developments in terms of watershed protection
<br />(Berke et al., 2003). Also, a modeling approach was
<br />used to predict runoff from low impact urbanization
<br />by estimating the ability of LID to infiltrate storm -
<br />water (Holman -Dodds et al., 2003). However, no stud-
<br />ies have monitored the effects of a LID design on
<br />stormwater runoff.
<br />This study, known as the Jordan Cove Urban
<br />Watershed project, investigated the effects of LID on
<br />stormwater quality and quantity. This paper reports
<br />the comparison of the quality and quantity of storm -
<br />water runoff from a traditional and a LID watershed
<br />during the postconstruction period. Previous papers
<br />have addressed the stormwater impacts during con-
<br />struction (Phillips et al., 2003), compared stormwater
<br />runoff from different driveway types (Gilbert and
<br />Clausen, 2006), and compared discharge lag times
<br />between traditional and LID watersheds (Hood et al.,
<br />2007).
<br />METHODS
<br />Study Site
<br />The project was located near the Long Island
<br />Sound in the town of Waterford, Connecticut. The
<br />watersheds studied consisted of a control and two
<br />watersheds (traditional and LID) that were studied
<br />prior to, during, and after residential development.
<br />The traditional watershed originally contained a
<br />poultry hatchery and storage buildings. During cali-
<br />bration, samples were collected at the discharge point
<br />of overland flow from a lawn. The LID watershed
<br />originally was a closed -out gravel pit. During calibra-
<br />tion, samples were collected at the discharge point for
<br />the restored pit. The treatment watersheds were
<br />adjacent and. the control watershed was 0.8 km away.
<br />Study watersheds were relatively small, with small
<br />lot sizes, gentle slopes, and total imperviousness
<br />varying, depending on the treatment (Table 1). The
<br />control watershed was developed in 1988 (Figure 1).
<br />The traditional watershed used minimum 0.2 ha lot
<br />zoning, a standard 8.5 m wide asphalt road, and a
<br />curb and gutter stormwater collection system
<br />(Figure 2). Roof runoff was directed to either grassed
<br />lawns or onto driveways. The LID watershed had
<br />26% open space, mostly along the periphery
<br />(Figure 3). Two main features of the design were the
<br />replacement of traditional curbs and gutters with
<br />grassed bioretention swales and the asphalt road
<br />with a narrower pervious concrete -paver road. A bio-
<br />retention cul -de -sac, which allowed for retention and
<br />infiltration of runoff, was used instead of the tradi-
<br />tional impervious asphalt area. Individual bioreten-
<br />tion areas (rain gardens) were incorporated into each
<br />lot to detain roof and lot runoff. These were designed
<br />to contain the first 2.54 cm of runoff from their indi-
<br />vidual watersheds. Shared driveways were used in 10
<br />of the 12 lots and were composed of asphalt, pervious
<br />concrete pavers, or crushed gravel. Cluster housing
<br />TABLE 1. Characteristics of Study Watersheds.
<br />FIGURE 1. Control Watershed Subdivision
<br />for the Jordan Cove Project, Connecticut.
<br />JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION 999 JAWRA
<br />Control
<br />Traditional
<br />LID
<br />Watershed area (ha)
<br />5.5
<br />2.0
<br />1.7
<br />No. of lots
<br />43
<br />17
<br />12
<br />Average lot size (ha)
<br />0.16
<br />0.15
<br />0.10
<br />% Total impervious
<br />29
<br />32
<br />22
<br />Average slope (%)
<br />1.0
<br />1.5
<br />1.8
<br />FIGURE 1. Control Watershed Subdivision
<br />for the Jordan Cove Project, Connecticut.
<br />JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION 999 JAWRA
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