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reduce pollutant loading and reduce impacts <br />to benthic biota may raise the allowable <br />imperviousness. However, even when <br />effective practices are widely applied, the <br />threshold of imperviousness is eventually <br />crossed, which results in a degraded <br />condition. It is, therefore, critical that local <br />government units (LGUs) address the <br />impacts of imperviousness very early on by <br />aggressive land use policies. <br />There are many policies that can be adopted <br />on a local level to reduce the impacts of <br />imperviousness. Narrower streets, smaller <br />parking requirements, swales instead of curb <br />and gutter, and a host of other practices are <br />outlined by documents from numerous <br />centers, associations and agencies. One of <br />the many growing practices is "Cluster <br />development." This is defined as the <br />grouping of all residential structures of a <br />development on a portion of the available <br />land, reserving a significant amount of the <br />site as protected open space. Many <br />communities in Minnesota and across the <br />United States are updating their <br />comprehensive plans and establishing <br />ordinances to guide the development and <br />construction of cluster developments. New <br />ordinances are requiring design standards, <br />and identifying open space and density <br />standards. These key changes have <br />prompted some communities to opt for more <br />descriptive terminology, such as "open - <br />space development" or "conservation <br />subdivision design," instead of the more <br />traditional "cluster development." While <br />this use of different terminology has created <br />some confusion, each still maintains the <br />three basic goals of cluster development: (1) <br />preserving open space, (2) protecting critical <br />ecological habitat and (3) preserving <br />agricultural land. <br />The useable open space created by a cluster <br />development can serve to meet a number of <br />community goals, such as the protection of <br />critical ecological resources, protection of <br />wooded areas or the preservation of <br />farmland. Obviously, these goals overlap <br />and have the potential to conflict with one <br />another. For example, the protection of <br />wildlife habitat may be incompatible with <br />the preservation of agricultural land. <br />However, the key benefit is the quality of <br />life preserved by the availability of open <br />space made possible through the clustering <br />of units. <br />POLICIES TO PROTECT GROUND <br />WATER <br />When development occurs, the problems of <br />runoff need to be addressed; often this is by <br />"management policies" or "infiltration <br />devices." Management policies, in this <br />context, means reducing impervious <br />surfaces, discharging impervious surfaces <br />over pervious areas, disconnecting roof <br />drains from the storm water system or other <br />measures. Management policies are <br />encouraged and are essential; however, <br />general policies may require special <br />considerations in industrial areas or other <br />unusual cases. <br />The other category of activity is called <br />infiltration devices. This is everything from <br />filter strips and swales to large infiltration <br />ponds or infiltration trenches, tubes or other <br />devices that conduct the runoff into the <br />ground. In most cases the types of devices <br />that are of most concern are devices that <br />bypass the zone of aeration above the <br />ground water table (vados zone) and <br />conduct surface runoff directly into the <br />ground. For example, swales and ditches <br />are generally of less concern, while devices <br />that conduct into deep aquifers are generally <br />of greater concern. Note that these are <br />generalizations that need to be evaluated on <br />a site - specific basis. A site analysis should <br />be conducted before implementing <br />infiltration devices on project or in a <br />community. <br />Infiltration devices, such as basins and <br />trenches, are controversial as BMPs for <br />storm water management. Literature <br />indicates ( e.g. see Pitt et al. January 1994) <br />that operation of infiltration devices is a <br />concern for two reasons: (1) failure to <br />Urban Runoff <br />11 -13 <br />