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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 <br />