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DISTANCE (IN FT.) YEAR 2000 L10 YEAR 2000 L50 <br />SITE <br />HOUSE <br />FROM CR 116 <br />DAYTIME NOISE <br />DAYTIME NOISE <br />RECEPTOR <br />(STATION) <br />NUMBER <br />CENTERLINE <br />LEVEL (dBA) <br />LEVEL dBA <br />44 <br />488+00 <br />3564 <br />9L <br />64 <br />5r <br />45 <br />489+40 <br />61 <br />66* <br />56 <br />46 <br />490+00 <br />3566-3568 <br />100 <br />63 <br />54 <br />47 <br />490+60 <br />3635 <br />122 <br />62 <br />53 <br />* Exceed 65 dBA. <br />Definitions and Standards: <br />The L10 reading is the sound level which is exceeded 10% of the time during the design <br />hnur. L50 is the level which is exceeded 50% of the time. In this study, the design <br />hour usea is the evening peak traffic hour. At other times during the day noise levels <br />are reduced due to lower traffic volumes. <br />Noise is measured in decibels adjusted to the human ear's sensitivity to different fre- <br />quencies (abbreviated dBA). For residential areas, the Federal Highway Administration <br />(FHWA) uses a standard of 70 dBA for L10 but has none for L50. The Minnesota Pollution <br />Control agency (MPCA) uses a daytime standard of 65 dBA fir L10 and 60 SBA for L50. <br />At none of the above sites will road noise exceed the Federal Highway Administration <br />(FHWA) standard of 70 dBA. None of the sites will be subjected to noise in excess of <br />the MPCA L50 standard of 60 dBA. Three of the sites, however, will experience noise in <br />excess of the MPCA L10 standard of 65 dBA. Site 5 will be 3dBA above, Site 42 will be <br />2 dBA above, and Site 45 will be 1 dBA above the MPCA standard. It is generally <br />accepted among noise experts, including the MPCA, that while the human ear can detect a <br />sudden change of as little as one dBA, a change of at least three or four dBA is needed <br />to detect a difference over a long perioJ of time. <br />Possible mitigation measures: <br />1. Alignment change. Unfortunately, any shift in horizontal alignment will merely <br />move the source of the noise (road traffic) closer to other nearby houses. A <br />significant shift in vertical alignment can't be accomplished because of the need <br />to match inplace cross roads and driveways. <br />2. Earth berms. Six feet of horizontal distance is needed for every foot increase in <br />height for earth berms (assumes 3:1 slopes on both sides). The three sites in <br />question range from 50 feet to 61 feet from the center of the road. Subtracting 30 <br />feet for the road and snow storage area leaves only 20 to 31 feet available for a <br />berm. The maximum height would be under 6 feet which is not high enough to reduce <br />noise below the 65 dBA level. <br />3. Noise walls. Reduction of noise to the 65 dBA level would require an 8 foot high <br />wall between each site and the road. The walls would need to be 400 or more feet <br />long and be continuous. Openings for driveways would destroy the noise reducing <br />effect of the walls. <br />Conclusions: <br />None of the sites will have noise levels above the 70 dBA FHWA standard. Of the 47 <br />sites along the road, none will exceed the MPCA L50 standard and only 3 will exceed the <br />65 dBA MPCA L10 standard, none of which will exceed it by more than 3dBA. Noise <br />mitigation measures are not recommended. <br />PB/DW;mak <br />09/29/89;PBNOISE 3 <br />