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Lake Minnetonka is dependent upon watershed runofT for all replenishment. <br />Lake Minnetonka is not fed by any spring or river inlet. All water is received from <br />precipitation falling within the immediate watershed. Most of this water enters the <br />Lake by direct runoff through a series of five major streams and their associated <br />lakes, marshland and sub-watersheds. Since the level of the Lake is generally below <br />the level of the ground water in the glacial deposits of the surrounding area, some <br />additional replenishment o curs from underground seepage, principally from the <br />many wetlands and marshy ponding areas along the shoreline. <br />Lake Minnetonka's ecology makes it easily susceptible to pollution hazards. The <br />combination of a single-source local water supply, relatively small watershed area, <br />many channel restrictions between separate bays, and a single outlet, have resulted <br />in Lake Minnetonka having an extremely long 25-year flush out period for complete <br />water change. This is second only to Lake Michigan in the region. The hazard is that <br />once pollutants enter the Lake, they tend to remain for a long time and they are not <br />easily diluted. <br />Lake Minnetonka has historically suffered from t^vo problems which directly <br />affect its environmental health and its value as a public amenity. One problem <br />w hich has been worsening with urbanization trends is a deterioration in water quality <br />caused by eutrophication. Eutrophication is the aging process by w hich natural waters <br />are enriched with nutrients that may stimulate excessive plant growth The plants <br />may be floating algae, attached algae, or rooted weeds. Eutrophication may occur <br />naturally, as sediments accumulate in lake basins over geologic time or it may be <br />induced artificially as a result of human activities, as in Lake Minnetonka. Much of <br />Lake Minnetonka has become more eutrophic during the last several decades the past <br />century, but sedimentation has been negligible. Instead, the accelerated <br />eutrophication of the Lake, w hich is due to increased inputs of nutrient elements, <br />particularly phosphorus and nitrogen, is evidenced by the increased grjwih of algae <br />and weeds. <br />The other problem is hydrologic instability. Because the lake level is dependent upon <br />precipitation, w ide ranges in water elevation have occurred over the years. During the <br />1930's. a general drought left the lake below normal level for 11 years with a <br />maximum decline of more than 6 feet. This low water condition caused the <br />con:.truction of deep wells for water augmentation and discussions about possible <br />diversion oftheCrow'River. A somew hat lesser drought durinu the late 1980's attain <br />raised concern about the instability of lake levels, vet the lake recovered from a 4- <br />foot drop in just two years without autimentation. <br />I <br />I <br />I <br />|Ni»< <br />t <br />CMP 3A - 3