Laserfiche WebLink
ASLESON, NESTINGEN, GULLIVER, HOZALSKI, AND NIEEIER <br />SITE SELECTION AND DESCRIPTIONS <br />Twelve sites in Minnesota were selected for the <br />development and evaluation of the rain garden <br />assessment during the 2006 field season (spring <br />through fall). These sites were selected based on the <br />following criteria: (1) permission and participation <br />from the owner /operator of the site, (2) availability of <br />site information (e.g., site plans, planting diagrams, <br />etc.), and (3) proximity to the University of Minne- <br />sota (UM). A summary of the rain garden character- <br />istics and the levels of assessment used at each site <br />are provided in Table 1. <br />The areas of the rain gardens ranged from 28 to <br />1,350 m The smallest rain garden was located in a <br />residential area and received stormwater runoff from <br />the street via a curb cut inlet. Several other rain <br />gardens received runoff from parking lot areas, or a <br />combination of stormwater runoff sources. Three rain <br />gardens were installed in the fall of 2003 and were <br />online (i.e., receiving runoff) in the spring of 2004. <br />Only the UM — Duluth (12) site had a pretreatment <br />practice installed, a sediment forebay located at the <br />inlet. Four of the rain gardens contained underdrains <br />to compensate for the restrictive soils in the area. <br />METHODS AND ANALYSIS <br />Visual Inspection <br />The rain gardens were examined for obvious drain- <br />age problems or impediments to infiltration, such as <br />ponded water present for more than 48 h after a rain- <br />fall event, sediment accumulation in the basin from <br />the drainage area, clogged inlet or outlet structures, <br />and excessive erosion within the rain garden. The <br />vegetation was then assessed with consideration of <br />the age of the :rain garden, time of the growing sea- <br />son, species present and their growth requirements, <br />and condition of the site. A visual assessment of the <br />health of the plants was made by examining and <br />recording the color, size, and quality of the leaves, <br />stem, and flowers. The available design plans along <br />with a plant field guide (Shaw and Schmidt, 2003) <br />were used to determine whether the correct species <br />were present. The percent vegetative cover was esti- <br />mated to determine if plants were established. The <br />sites were also inspected for the presence of wetland <br />plant species (e.g., cattail, arrowheads, and marsh <br />smartweed) to determine if hydric soils may be pres- <br />ent, indicating prolonged periods of saturation. Photo- <br />graphs of each site were taken and observations <br />made were recorded to develop a complete record of <br />conditions at the time of assessment. <br />The depth at which rain gardens are installed var- <br />ies greatly and is dependant on local factors such as <br />drainage area, surface area available for the rain gar- <br />den, and underlying native soil type. To determine <br />the existing soil profile a single soil core was taken at <br />each rain garden near the center of the basin (as a <br />representative sample) to a depth of —1.2 m. This <br />was the maximum depth a standard auger could pen- <br />etrate using a soil corer and was believed to be suffi- <br />cient to profile the near - surface soils that are <br />important to infiltration. The textures of the different <br />soil layers in the core were determined in the field <br />using the feel method (Thien, 1979) and the USDA <br />Textural Triangle. The color of the soil from each <br />distinct layer in the core was determined by match- <br />ing with a color chip in a Munsell soil -color charts <br />(X -Rite, Grand Rapids, Michigan). Special attention <br />was paid to soils that were gray in color or contain <br />TABLE 1. General Description of the Assessed Rair. Gardens <br />ID <br />Rain Garden Name <br />Size (m <br />Level of Assessment <br />Year Built <br />Source of Urban Runoff <br />1 <br />Burnsville <br />28 <br />1 and 2 <br />2003 <br />Residential street <br />2 <br />RWMWD #4 <br />29 <br />1 and 2 <br />2006 <br />City street and office building roof <br />A' <br />46 <br />1 <br />1999 <br />Parking lot and turf <br />3 <br />B' <br />50 <br />1 <br />2001 <br />Residential street <br />4 <br />5 <br />RWMWD #5 <br />59 <br />1, 2, and 3 <br />2006 <br />City street and office building roof <br />6 <br />UM — St. Paul <br />67 <br />1, 2, and 3 <br />2004 <br />Turf and street <br />7 <br />Cottage Grove <br />70 <br />1, 2, and 3 <br />2002 <br />Parking lot <br />8 <br />C 1 <br />140 <br />1 <br />2001 <br />Residential street <br />9 <br />RWMWD #1 <br />147 <br />1 and 2 <br />2006 <br />City street and office building roof <br />D <br />180 <br />1 <br />2001 <br />Residential street <br />10 <br />11 <br />Thompson Lake <br />278 <br />1 and 2 <br />2003 <br />Parking lot <br />12 <br />UM — Duluth <br />1,350 <br />1 and 2 <br />2005 <br />Parking lot <br />Notes: RWMWD, Ramsey - Washington Metro Watershed District; UM, University of Minnesota <br />'Permission to publish the locale of these sites was not obtained. <br />JAWRA 1022 JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION <br />