•Runoff and                      Phosphorus                  load for forest              and residential            land
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   A land area cleared for agricultural, residential, or commercial use contributes more to nutrient loading than a naturally vegetated area, such as forested land (Dennis1986).  The combination of vegetation removal and soil compaction involved in the clearing of land results in a significant increase in surface runoff, which amplifies the erosion of sediments carrying nutrients and pollutants of human origin.
   Naturally vegetated areas offer protection against soil erosion and surface runoff (Firmage, pers comm).  The forest canopy reduces erosion by diminishing the direct physical impact of rain on soil.  The root systems of trees and shrubs reduce soil erosion by decreasing the rate of runoff, allowing water to percolate into the soil.  Roots decrease the nutrient load in runoff through direct absorption of nutrients for use in plant structure and function.  Due to these features, a forested area acts as a buffering system by decreasing surface runoff and absorbing nutrients before they enter water bodies.
  Evidence of increased surface runoff due to development and consequent effects on nutrient transport is presented in a study concerning phosphorus loading in Augusta, Maine (Figure IIB2a).  The study revealed that surface runoff from a residential area contained ten times more phosphorus than runoff from an adjacent forested area.  The study concluded that the surface-runoff flow rate of residential area can be in excess of four times the rate recorded for forested land. Top: volume of immediate runoff over a 12 hour period; Middle: phosphorus concentration in the runoff; Bottom: total amount of phosphorus exported into local streams and lakes from the storm (Dennis 1986).
Activities that remove the cover of the canopy and expose the soil to direct rainfall increase erosion.  Two studies by the Land Use Regulation Commission on tree harvesting sites noted that erosion and sedimentation problems occurred in 50 percent of active and 20 percent of inactive logging sites selected (MDC 1983).  Skidder trails may pose a problem when they run adjacent to or through streams