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Agenda - Council - 06/13/2017
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Agenda - Council - 06/13/2017
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Meetings
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Agenda
Meeting Type
Council
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06/13/2017
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All modeled nighttime impacts are within the NAC-2 standards. Therefore, assuming the <br />proposed residences will have year-round climate control, the modeled impacts at the proposed <br />development are within the State noise standards and no additional mitigation is required. <br />V. Railroad Noise Impacts <br />Based on the noise monitoring data collected during train pass-bys, the trains are not generally <br />expected to cause exceedances of the State Noise standards. Analysis of time history data for the <br />train pass-bys show that the full length trains cause elevated noise levels (above 64.5 dBA) for <br />about 90 to 110 seconds. Without, the proposed berm, it would take four or more full length <br />trains passing by in an hour to approach the 6 minutes of impact required for the Lio <br />exceedances. One to three full length trains passed by per hour during the monitoring. This is <br />consistent with MnDOT rail traffic information for this track. Therefore, train noise is not likely <br />to cause the Minnesota noise standards to be exceeded in a way that requires additional <br />mitigation. <br />VI. Summary and Conclusions <br />Riverstone Development, LLC is proposing a residential development in Ramsey, Minnesota. <br />The proposed project location is bordered on the south by Minnesota Highway 10 (TH 10) and a <br />Burlington Northern railroad track. The proposed project location and layout is shown in Figure <br />1. Because of the potential noise impacts from TH 10 traffic , the City of Ramsey as requested a <br />noise study to evaluate the proposed project relative to Minnesota Noise Standards. <br />The project is proposing a berm between the residential area and the highway and railroad. <br />Post -development noise levels were predicted for 19 receptor locations using monitoring data <br />and computer modeling <br />The modeled noise level at one of the 19 receptor locations exceeds the Minnesota NAC-1 <br />standards for daytime hours. The modeled noise level at all but one of the receptor locations <br />exceeds the Minnesota NAC-1 standards for nighttime hours. <br />The NAC-1 daytime standards are designed to prevent speech interference in areas for outdoor <br />activities. Areas for outdoor activities are not allowed if these noise levels are exceeded. The <br />modeled L50 noise level at Receptor R1A exceeds the State standard by just 0.4 dBA. Remedies <br />could include 1) having no areas for outdoor use in the portion of the property facing the <br />roadway, 2)a barrier (solid fence) around all or a portion of the yard or patio at this home <br />blocking the line of site between the vehicles on the road and an area designated for outdoor use <br />or, 3) extending the proposed berm to provide additional mitigation at this location. <br />The nighttime NAC-1 standards are designed to prevent sleep interference for people sleeping in <br />bedrooms with partially open windows. NAC-2 nighttime standards apply to NAC-1 locations if <br />the building is constructed in such a way that the exterior to interior sound level attenuation is at <br />least 30 dBA and the building has year-round climate control. Buildings meeting the State <br />building code requirements typically meet the 30 dBA exterior to interior sound level attenuation <br />requirement. <br />
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