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<br />from the USGS report on types of homes and wastewater flows, <br />as well as the age of the homes, well logs of the drinking <br />water wells, septic tank and well spacing, and previous land <br />use in the area was not available. However, based on the <br />findings of the USGS study (referenced in the DEIS) and <br />based on new information derived since the DEIS was <br />produced, some trends are becoming apparent. <br /> <br />I <br />l <br /> <br />It appears the highest nitrate concentrations are found in <br />shallow aquifers in areas that have irrigated, cultivated, <br />agricultural land use. The lowest nitrate concentrations <br />are found deeper in the drift in non-residential, <br />non-agricultural areas (considered background levels). <br />Nitrate concentrations in residential areas rank third, <br />after cultivated, non-irrigated land use. This was the <br />ranking suggested by the USGS findings and these results are <br />somewhat supported by a study being conducted by the Anoka <br />County Health Department as well as other studies performed <br />in sandy soils. <br /> <br />The Anoka County study, still in progress, is examining an <br />area about one mile northeast of Northfork. Some drinking <br />water wells in a residential area about two square blocks in <br />size have elevated nitrate levels ranging from 3.5 to 33 <br />mg-N/l. Wells are about 7B to 8B feet deep. However, the <br />development is only about five years old. Rough <br />calculations (using Brown et. ale and MPCA 1984 as a guide) <br />would indicate that septic tank systems would not be able to <br />produce the high nitrate concentrations at those depths in <br />five years. In this case, previous land use practices may <br />be a factor; this site in Ramsey was previously an <br />irrigated, cultivated agricultural area. The one deep well <br />(155 feet) in the study area nad .nitrate nitrogen <br />concentrations of less than 1.B mg/l. <br /> <br />\ <br /> <br />Other studies conducted in outwash sands find similar <br />trends. In three cases, where residential onsite systems <br />coincided with various agricultural land use (nursery <br />production, poultry raising, cherry orchards), agricultural <br />land use was the most important source of nitrate <br />contamination. However, deep wells (greater than 3B meters) <br />typically had low nitrate concentrations (Matisoff et. ale <br />no date, Ritter and Chirnside 1984, and USEPA 1982). <br /> <br />r . <br />I <br />I <br /> <br />Northfork drinking water wells appear to have a moderate <br />risk for nitrate contamination. Eighty acres of corn have <br />been fertilized with 75 Ibs of nitrogen/acre. 2BB acres of <br />soybeans and lsB acres of oats are in production, but have <br />not been fertilized. No irrigation has been used. Prior to <br />1984, this acreage was owned by General Mills and land was <br />leased for farming. Farming practices are not known for the <br />years prior to 1984. <br /> <br />-77- <br /> <br />I <br /> <br />........... <br />