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�,� ll�dr<>carhonsl. and ,ill plumes (�edinlen- <br /> citil,n i. all <>f which affect the entire food <br /> chain C[ild the species abundance and <br /> diver-,in-of aquatic life. including fish (8). The in- <br /> tcraction of these problems distinguish <br /> urban streams (3). <br /> For stormwater management to compre- <br /> Riparian Fonts Buffer <br /> llensiv ely protect the quality of streams. it <br /> needs to address the multiplicity of prob- —RasofiInflow P* <br /> lems, rather than solely controlling peak Woody wetlaAd <br /> tlo%vs" The interaction of problems offers an water Lerel <br /> Opportunity to solve a range of problems si- �\ <br /> nlultaneously, as the following descriptions Seu De edt potlrs <br /> illustrate. <br /> l�efditdm Yrrwhet Lard Sprwder <br /> Controlling increases in runoff peaks. <br /> Many municipalities have passed ordinances <br /> requiring that post-development runoff Figure 4.A"wooded wetland with infiltration trenches"as a functional <br /> peaks not exceed pre-development peaks. landscape enhancement. <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 (44 in). After infiltration, 30 cm/yr (12 in/yr) <br /> -play it safe," municipalities often set as a of this total reemerges to support the base <br /> design standard the control of the 10 to 100 flow of streams. Low density single family <br /> year frequency storms with outlet devices so residential development with an impervious- <br /> big that they pass, unchecked, smaller ness of 20 percent has been shown to re- <br /> storms of two- to five-year frequency, which duce this base flow by 12 percent to 27 <br /> are the cause of much of the flood damages cm/yr (10.6 in/yr) while commercial devel- <br /> experienced today. opment with an imperviousness of 90 per <br /> Even when designed to also control small- cent would reduce it by 90 percent to 3 <br /> er storms, detention basins do not reduce cm/yr(1.2 in/yr) (5). <br /> the volume of-runo ,­ancl only control peak The use of stormwater infiltration devices <br /> rates o ow. Most of the thous;m of de- that infiltrate the first 1.25 cm (.5 in) of <br /> tention basins found in the areas surround- runoff would maintain 29 cm/yr (11.6 in/yr) <br /> ing our cities are constructed as so-called of post development base flow (96 percent) <br /> -dry basins" that do not improve the quality for single family residential uses and 22 <br /> Of urban runoff. Often unsightly, such basins cm/yr (8.7 in/yr) (72 percent) of the base <br /> are usually found in far corners, using left flow on commercial sites (5). As indicated <br /> over spaces of subdivisions. Alternatives to earlier, maintaining such base flow is partic- <br /> standard dry basins are "extended detention ularly important for headwater streams. <br /> basins" and -wet basins" with a permanent Problems with standing water such as expe- <br /> pools that offer water quality improvement. rienced in Maryland can be designed out <br /> Such urban ponds are an aesthetic enhance- (2). <br /> ment and have been found to more than Infiltration provides the added benefit of <br /> double adjacent property values (11). They water—quality enhancement as impurities in <br /> are a delight for urban residents and provide the "first"mush""of runoff are filtered. Infiltra- , <br /> habitat for water related wildlife. A survey in tion can be accomplished through measures <br /> Columbia, Maryland, found that 75 percent that enhance the landscape, such as the <br /> of homeowners preferred "wet ponds" for woody wetland with infiltration trenches <br /> stormwater management while only 17 per- shown in Figure 4. <br /> cent liked dry detention basins. Residents Controlling runoff pollution. The Clean <br /> overwhelmingly (94 percent) felt that it is Water Act has set goals to make the Nation's <br /> desirable to manage future stormwater waters fishable and swimmable. The Nation- <br /> basins for fish and wildlife as well as for wide Urban Runoff Program (13) has docu- <br /> flood and sediment control (1). mented the severity of the problem, and <br /> Preventing losses in infiltration. To models have been developed based on its <br /> control the increased volume of runoff leav- findings. This includes a highly practical <br /> ing a site, and not lust t e higher peak "Simple Formula" set forth by the Metropoli- <br /> tps can be taken to maintain mfltra- tan Washington Council of Governments (7) <br /> tion. Figure 3 presents a water bu get- that that permits the quantification of runoff pol- <br /> sFi-ows how groundwater recharge is re- lution loading for development sites. <br /> duced by impervious surfaces, while runoff The major sources of runoff pollution <br /> volumes rise. Annual precipitation in many from urban areas are impervious surfaces <br /> sections of Maryland, for example, is 112 cm that collect nitrogen deposited through acid <br /> JANUARY-FEBRUARY 1994 17 <br />