My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
12-03-25 PC Packet
ArdenHills
>
Administration
>
Commissions, Committees, and Boards
>
Planning Commission
>
Planning Commission Packets
>
2025
>
12-03-25 PC Packet
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
11/26/2025 4:28:30 PM
Creation date
11/26/2025 4:27:51 PM
Metadata
Fields
Template:
General
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
52
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
<br /> <br />Boston Scientiffc <br />Report: ABN-1487A <br />7/28/2024 <br />Page 2 <br /> <br />SUMMARY <br />Boston Scientiffc commissioned follow-up sound monitoring at its Arden Hills manufacturing site, speciffcally <br />Building #14, in response to prior nighttime assessments conducted near the northwest corner of the same <br />building. <br />On July 17–18, 2025, Sound Inspectors deployed a sound analyzer to continuously monitor noise levels at the <br />same approximate location used in previous studies—approximately 11 feet high in a tree along the walking path. <br />This site was previously determined to be the closest secure point between the mechanical room of Building #14 <br />and the nearest residence on Wynridge Drive. <br />During the monitoring period, sound levels at the designated measurement location ranged from an LAeq of 49.5 <br />dBA to 68.0 dBA. Elevated readings were primarily attributed to transient sources, including freeway and local <br />tralfic, horns, lawn mowers, sprinkler systems, and pedestrian activity along the nearby path. The lowest levels <br />were consistently observed during nighttime hours when external human -generated noise was minimal. <br />According to Boston Scientiffc, the rooftop mechanical equipment on Building #14 operates continuously. <br />Therefore, the lowest recorded sound levels during quiet nighttime intervals are reasonably assumed to reifect the <br />dominant noise contributions from the building itself. <br />To better isolate building-generated sound from background transients, data was collected at one-minute <br />intervals. These high-resolution measurements enabled calculation of LA10 and LA50 values per interval, which <br />were then aggregated to hourly metrics using the arithmetic mean. <br /> <br /> Table 1 -Hourly Nighttime Ln Average <br /> 2025-July 17 2025-July 18 <br />Time L10 L50 L10 L50 <br />12 AM 50.2 49.7 52.4 51.7 <br />1 AM 50.2 49.8 52.0 51.5 <br />2 AM 50.2 49.8 53.9 53.1 <br />3 AM 50.2 49.8 54.9 53.8 <br />4 AM 50.5 50.1 54.3 53.4 <br />5 AM 51.5 51.1 54.6 53.9 <br />6 AM 54.0 52.8 54.8 54.1 <br />10 PM 52.6 51.9 <br />11 PM 52.2 51.6 <br /> <br />As shown in Table 1, LA50 values during four hourly nighttime intervals on July 17 fell below the Minnesota <br />Pollution Control Agency (MPCA) Noise Area Classiffcation 1 threshold of 50. Additionally, all hourly LA10 <br />measurements remained within the applicable state standard on both monitoring dates. These patterns suggest <br />that transient peak noise events were effectively limited during the measurement period, and the results are <br />reasonably representative of background noise generated by Building #14’s continuously operating equipment.
The URL can be used to link to this page
Your browser does not support the video tag.