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hw 1jrc'carbons). and silt plumes t•edimen- <br />tation ).` all of which affect the entire food <br />chain and the species abundance and diver- <br />.it }' of aquatic life. including fish (8 . The in- <br />teraction of these problems distinguish <br />urban stream., (3). <br />For stormwater management to compre- <br />hensively protect the quality of streams. it <br />needs to address the multiplicity of prob- <br />lems. rather than solely controlling peak <br />flows. The interaction of problems offers an <br />opportunity to solve a range of problems si- <br />multaneously, as the following descriptions <br />illustrate. <br />Controlling increases in runoff peaks. <br />Many municipalities have passed ordinances <br />requiring that post - development runoff <br />peaks not exceed pre - development peaks. <br />This is accomplished by detaining and then <br />releasing accumulated runoff through a <br />basin outlet device sized to pass flows at <br />pre - development rates. In an attempt to <br />-play it safe," municipalities often set as a <br />design standard the control of the 10 to 100 <br />year frequency storms with outlet devices so <br />big that they pass, unchecked, smaller <br />storms of two- to five -year frequency, which <br />are the cause of much of the flood damages <br />experienced today. <br />Even when designed to also control small- <br />er storms, detention basins do not reduce <br />the volume of -runoff, and only control peak <br />`aces & flow. Most of the thousan .sd; of de- <br />tenti o basins found in the areas surround- <br />ing our cities are constructed as so- called <br />-dry basins" that do not improve the quality <br />of urban runoff. Often unsightly, such basins <br />are usually found in far comers, using left <br />over spaces of subdivisions. Alternatives to <br />standard dry basins are "extended detention <br />basins" and -wet basins" with a permanent <br />pools that offer water quality improvement. <br />Such urban ponds are an aesthetic enhance- <br />ment and have been found to more than <br />double adjacent property values (11). They <br />are a delight for urban residents and provide <br />habitat for water related wildlife. A survey in <br />Columbia, Maryland, found that 75 percent <br />of homeowners preferred "wet ponds" for <br />stormwater management while only 17 per- <br />cent liked dry detention basins. Residents <br />overwhelmingly (94 percent) felt that it is <br />desirable to manage future stormwater <br />basins for fish and wildlife as well as for <br />flood and sediment control (1). <br />Preventing losses in infiltration. To <br />control the increased volume of runoff leav- <br />ing a site, and not lust the higher peak <br />flt,ws, ste s can be taken to maintain infiltra- <br />tion'. ure 3 presents a Nvater budget that <br />sFiows how groundwater recharge is re- <br />duced by impervious surfaces, while runoff <br />volumes rise. Annual precipitation in many <br />sections of Maryland, for example, is 112 cm <br />Riparian Forest Buffer <br />Figure 4. A "wooded wetland with infiltration trenches" as a functional <br />landscape enhancement. <br />(44 in). After infiltration, 30 cm/yr (12 in/yr) <br />of this total reemerges to support the base <br />flow of streams. Low density single family <br />residential development with an irnpervious- <br />ness of 20 percent has been shown to re- <br />duce this base flow by 12 percent to 27 <br />cm/yr (10.6 in/yr) while commercial devel- <br />opment with an imperviousness of 90 per- <br />cent would reduce it by 90 percent to 3 <br />cm/yr (1.2 in/yr) (5). <br />The use of stormwater infiltration devices <br />that infiltrate the first 1.25 cm (.5 in) of <br />runoff would maintain 29 cm/yr (11.6 in/yr) <br />of post development base flow (96 percent) <br />for single family residential uses and 22 <br />cm/yr (8.7 in/yr) (72 percent) of the base <br />flow on commercial sites (5). As indicated <br />earlier, maintaining such base flow is partic- <br />ularly important for headwater streams. <br />Problems with standing water such as expe- <br />rienced in Maryland can be designed out <br />(2). <br />Infiltration rovides the added benefit of <br />water qu iry enhancement as impurities in <br />the "firsh" of runoff are filtered. Infiltra- <br />tion can be accomplished through measures <br />that enhance the landscape, such as the <br />woody wetland with infiltration trenches <br />shown in Figure 4. <br />Controlling runoff pollution. The Clean <br />Water Act has set goals to make the Nation's <br />waters fishable and swimmable. The Nation- <br />wide Urban Runoff Program (13) has docu- <br />mented the severity of the problem, and <br />models have been developed based on its <br />findings. This includes a highly practical <br />"Simple Formula" set forth by the Metropoli- <br />tan Washington Council of Governments (7) <br />that permits the quantification of runoff pol- <br />lution loading for development sites. <br />The major sources of runoff pollution <br />from urban areas are impervious surfaces <br />that collect nitrogen deposited through acid <br />JANUARY- FEBRUARY 1994 17 <br />