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<br />Over Excavation (aka soil correction) at Rolling Hills’ Existing Soil Treatment Area <br />Dan Wheeler – UM Soil Scientist <br /> <br />Knowns: <br />1. The native and natural soils across the entire mowed grass area are drumlin-like in their characteristics. This <br />means that they naturally perch water (have saturated soil conditions) seasonally within 12” of the soil surface. <br />Underlying these unsuitable wet soil conditions is many feet of densely compacted glacial deposit of varying <br />textures including clay and clay loams as verified during earlier fall 2020 soil pits dug and described. These soils <br />do not allow for water movement, which is why there is saturation evident in the overlying soils. These very <br />similar soils were observed in their more natural state on the north side of the Rolling Hills property just north of <br />the trail off of Cleveland Avenue. <br />2. The soils across this entire mowed grass area have been compromised by previous activities on this site. <br />a. There are severely compacted soils from agricultural and/or construction activities. <br />b. There are areas closer to Jarvis Street that have the presence of fill in wetland areas as verified during <br />earlier fall 2020 soil pits dug and described. <br />c. Existing wastewater does not infiltrate/move vertically into and through these soils and has likely <br />plugged any voids with solids. <br />3. Clearly, the status of the soil resource in the entire mowed area is problematic. <br />Solutions: <br />1. Removal and correction of the problem soil. <br />a. This effort will remove some compacted and/or clayey soil. <br />b. Any replacement soil would have to be able to withstand placement with minimal compaction – MN <br />Rule Chapter 7080 specifications limit this to clean sand. <br />c. This effort will not remove or change the fact that water is moving in the landscape. Digging a large hole <br />in relatively impermeable materials and filling it full of different material creates a bathtub in the <br />landscape. Water will not be able to move into the surrounding unexcavated soils so will fill the new <br />area with water. In addition, the filled wetlands are still wet as was evidenced by gley soil conditions <br />(permanent saturated conditions) during our earlier fall 2020 soil pit in this area and will add to the <br />water in this area. <br />2. Underdrains to lower and/or drain water (in addition to soil removal/correction). <br />a. MPCA has considered any artificial drainage within the area of a wastewater soil treatment area to <br />require a surface discharge permit known as a National Pollution Discharge Elimination (NPDES). This <br />moves the project into another permitting group with the MPCA and would require additional design, <br />monitoring, reporting, etc. along with larger permitting fees. This is considered a tall hurdle by many and <br />is one way the MPCA discourages such a solution (see attached MPCA factsheet). <br />b. In addition, saturated soil elevation does not necessarily lower with an underdrain. Underdrains provide <br />an easier outlet for the water. Additional work would be required to verify. A drainage maintenance <br />agreement would also be required. <br />c. The elevation of the periodically saturated soil will remain the same on the site for the design of a new <br />system. There will not be any credit given to any fill material that is at or below the original soil surface <br />as the surrounding soils remain and possess this limiting soil condition. This means mounds would still <br />be required to be constructed similar to earlier discussions, layouts, etc. <br />3. Find a natural soil condition that is favorable for treatment and acceptance of wastewater. <br />a. Allows for the use of established 7080/7081 design practices. <br />b. Provides a greater certainty of long-term performance and life span. <br />c. There will be a simplified permitting process <br />