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•Minnesota <br />Pollution <br />Control <br />Agency <br />Environmental <br />Outcomes <br />Division <br />Ground Water <br />Monitoring & <br />Assessment <br />Program <br />Estimating Ground Water <br />Sensitivity to Nitrate Contamination <br />Water resource managers often view ground <br />water pollution sensitivity maps as an <br />important tool for ground water protection. <br />Methods for mapping sensitivity consider <br />factors such as soil permeability, aquifer <br />conductivity, depth to water, and recharge. <br />Sensitivity ratings are based on the time it <br />takes for water to travel from a point of <br />origin (for example, a septic system or a <br />farm field) to the water table or an aquifer. <br />Sensitivity methods based strictly on time of <br />travel provide little information about the <br />potential fate of contaminants in ground <br />water. For example, nitrate can be <br />transformed in ground water through a <br />process called "denitrification." <br />Denitrification reduces potential negative <br />effects of nitrate on drinking water or surface <br />water receptors. <br />The Ground Water Monitoring and <br />Assessment Program (GWMAP) of the <br />Minnesota Pollution Control Agency <br />(MPCA) has collected data that suggest <br />denitrification is an important process in <br />ground water. Denitrification occurs within <br />well- defined conditions in ground water. <br />Assessing these conditions is an important <br />tool for water managers, and is more useful <br />in aquifer management than simple estimates <br />of hydrologic sensitivity. `Geochemical <br />sensitivity" is the term we <br />June 1999 <br />use to describe sensitivity of ground water to <br />nitrate contamination. <br />Under what conditions is an aquifer <br />sensitive to nitrate contamination? <br />In Minnesota, surficial aquifers are <br />recharged annually. This means the time it <br />takes water to move from a point of origin to <br />the water table is less than one year. By <br />traditional mapping techniques, these <br />surficial aquifers are considered sensitive to <br />nitrate contamination. Resource managers, <br />in turn, may use these sensitivity estimates <br />for water planning, even though deeper <br />portions of these aquifers may not be <br />sensitive because nitrate will be denitrified. <br />Recharge and infiltration certainly affect the <br />fate of nitrate in the environment, but we <br />emphasize the importance of characterizing <br />the aquifer chemistry to predict the fate of <br />nitrate. These concepts are explained in <br />greater detail in a report (MPCA, 1998a). <br />The following table can be used as a rough <br />guide to identify ground water that is <br />sensitive to nitrate contamination. <br />When using this table, all three criteria <br />must apply for a ground water sample to <br />be classified as sensitive or not sensitive. <br />This is important, because we have observed <br />mixed results for many samples. Dissolved <br />oxygen and oxidation - reduction potential <br />Characteristic <br />Sensitive <br />Not sensitive <br />Filtered iron concentration <br />Less than 0.1 part per million <br />More than 1 part per million <br />Eh <br />More than 250 millivolts <br />Less than 225 millivolts <br />Dissolved oxygen <br />More than 1 part per million <br />Less than 1 part per million <br />Minnesota Pollution Control Agency, 520 Lafayette Rd. N., Saint Paul, MN 55155 -4194 <br />(651) 296 -6300, toll -free (800) 657 -3864, TTY (651) 282 -5332 or (800) 657 -3864 <br />This material can be made available in alternative formats for people with disabilities. <br />Printed on rervnled naner nnntaininn at least 20 nement fihers from nanar recvc:Ied by consumers. <br />