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HomeMy WebLinkAbout5.b. Dakota Aggregates 2016 Large Scale Mineral Extraction Permit Renewal20165 Large Scale Mineral Extraction Annual Operating Permit Agreement for Dry/Wet Mining Sub-phases 1A, 1B, 1C, 2A and 2B, 2C and 2D; and North Dry Mining Sub-phases 1A, 1B, 2C and 2D DAKOTA AGGREGATES, LLC A. Dakota Aggregates, LLC (hereinafter "the Operator") signs a written consent to these conditions binding itself and its successors, heirs or assigns to the conditions of said permit. B. The term of the permit shall extend from January 1, 20165 until December 31, 20165 unless revoked prior to that for failure to comply with the permit requirements. C. Mining in Wet/Dry Mining Sub-phases 1A, 1B, 2A, and 2B may occur 24 hours a day, 7 days a week. D. Mining and screening in North Dry Mining Sub-phases 1A, 1B, 1C, 2A, 2B, 2C, and 2D may occur 24 hours a day, 7 days a week. E. Trucks may haul from North Dry Mining Sub-phases 1A, 1B, 1C, 2A, 2B, 2C, and 2D from 6 a.m. to 10 p.m. Monday through Friday and 7 a.m. and 7 p.m. Saturday , except for hauling outside those hours for the execution of a contract requirement of up to five (5) MnDOT or other public agency roadway construction project. During the execution of the MnDOT or other public contracts, the hauling may occur 24 hours a day, 7 days a week. F. No crushing or washing equipment shall be located or used in the North Dry Mining Sub-phases 1A, 1B, 1C, 2A, 2B, 2C, and 2D. G. The North Dry Mining Sub-phases 1A, 1B, 2C, 2A, 2B, 2C, and 2D shall not be mined below the 882 foot elevation. H. Protection equipment that is installed on hauling trucks, such as covers for the truck beds, shall be used while traveling on public roads. Non-use will be considered a violation of the permit condition. I. Trucks shall not use any locally designated road as part of their haul route except for the shortest route between the delivery site and the nearest County, State or U.S. highway. J. Trucks may not be loaded heavier that the public haul roads posted weight restrictions. K. Engineered designs for any reclamation steeper than a 3 to 1 slope must be submitted and approved by the City Engineer before the reclamation can occur. 20165 Annual Operating Permit Dakota Aggregates, LLC 2 of 5 L. A gate and thirty (30) feet of fencing on each side of the gate shall be installed at the Station Trail access. The gate shall be closed and locked when the mining or ancillary uses are not in operation. A knox box or similar devise shall be installed to provide emergency personal access to the key for the lock. M. Conformance with the City Engineer’s Memorandum dated September 20, 2012. N. The University of Minnesota (or designated entity) shall obtain approval and/or concurrence from the MPCA regarding completion of appropriate investigations and/or actions taken in response to identified releases of hazardous substances, pollutants or contaminates as defined under Minn. Statute 115B, and as deemed reasonable and necessary by the MPCA. O. Dakota Aggregates shall clean dirt and debris from streets that has resulted from extraction or hauling operations related to the Mineral Extraction Permit. After Dakota Aggregates has received 24-hour verbal notice, the City will complete or contract to complete the clean-up at Dakota Aggregates’ expense. In the event of a traffic hazard as determined by the City Administrator (or the Administrator’s designee) or Rosemount Police Department, the City may proceed immediately to complete or contract cleanup at Dakota Aggregates’ expense without prior notification. P. No topsoil shall be removed from the site unless Dakota Aggregates can demonstrate that there is topsoil in excess of the amount needed to reclaim the End Use Grading Plan with at least six (6) inches of topsoil. Dakota Aggregates shall take necessary measures to prevent erosion of the stockpiled topsoil. Q. Any costs incurred now or in the future in changing the location of existing public or private utilities including but not limited to pipelines, transmission structures and sewer infrastructure located within the permit area shall be the sole obligation and expense of Dakota Aggregates. R. All costs of processing the permit, including but not limited to planning fees, engineering fees, and legal fees, shall be paid by Dakota Aggregates prior to the issuance of the permit. Dakota Aggregates shall reimburse the City for the cost of periodic inspections by the City Administrator or any other City employee for the purpose of insuring that conditions of the permit are being satisfied. Dakota Aggregates agrees to reimburse the City for any other costs incurred as a result of the granting or enforcing of the permit. S. Dakota Aggregates shall deposit with the Planning Department a surety bond or cash deposit in the amount of Eight Hundred Fifty One Thousand one Hundred Dollars ($851,100) in favor of the City for the cost of restoration, regrading and/or revegetating land disturbed by mining activities and to ensure performance of all requirements of this resolution and City ordinances by Dakota Aggregates. The required surety bonds must be: 1. With good and sufficient surety by a surety company authorized to do business 20165 Annual Operating Permit Dakota Aggregates, LLC 3 of 5 in the State of Minnesota. 2. Satisfactory to the City Attorney in form and substance. 3. Conditioned that Dakota Aggregates will faithfully comply with all the terms, conditions and requirements of the permit; all rules, regulations and requirements pursuant to the permit and as required by the City and all reasonable requirements of the City Administrator (or the Administrator’s designee) or any other City officials. 4. Conditioned that Dakota Aggregates will secure the City and its officers harmless against any and all claims, for which the City, the Council or any City officer may be made liable by reason of any accident or injury to persons or property through the fault of Dakota Aggregates. 5. The surety bond or cash escrow shall remain in effect from January 1, 20165 until July 31, 20176. Once the interim reclamation grades and vegetation have been established and approved by the City, the bond may be reduced by Five Hundred Sixty Seven Thousand Four Hundred Dollars ($567,400 = 113.48 acres times $5,000 per acre). Once the end use grading grades and vegetation have been established and approved by the City, the bond may be reduced by Two Hundred Eighty Three Thousand Seven Hundred Dollars ($283,700 = 113.48 acres times $2,500 per acre). Upon thirty (30) days’ notice to the permit holder and surety company, the City may reduce or increase the amount of the bond or cash deposit during the term of this permit in order to insure that the City is adequately protected. T. A landscape security of $42,625 (155 trees times $250 per tree times 110%) shall be provided. After the trees have been established, $38,362 (90%) of the landscaping security can be released. The final $4,263 (10%) shall be maintained through the existence of the berm for Dry/Wet Sub-Phase 1A and 2A to ensure that as trees die, that those trees are replaced. The landscaping security shall be in the form of a letter of credit in favor of the City or cash escrow. U. Dakota Aggregates shall furnish a certificate of comprehensive general liability insurance issued by insurers duly licensed within the State of Minnesota in an amount of at least Five Hundred Thousand and no/100 ($500,000.00) Dollars for injury or death of any one person in any one occurrence, and at least One Million Five Hundred Thousand and no/100 ($1,500,000.00) Dollars for injury or death of more than one person arising out of any one occurrence and damage liability in an amount of at least Two Hundred Fifty Thousand and no/100 ($250,000.00) Dollars arising out of any one occurrence. The policy of insurance shall name the City as an additional insured and shall remain in effect from January 1, 20164 until July 31, 20175. V. Dakota Aggregates shall hold the City harmless from all claims or causes of action that may result from the granting of the permit. Dakota Aggregates shall indemnify the City for all costs, damages, or expenses, including but not limited to attorney's fees that the City may pay or incur in consequence of such claims. W. Dakota Aggregates shall submit to the City semi-annually a written report indicating 20165 Annual Operating Permit Dakota Aggregates, LLC 4 of 5 the amount of material extracted from the site for the prior six-month period. After said written report is submitted, the City shall perform an inspection of the site to confirm compliance with the conditions within the Annual Operating Permit. X. Reclamation requires the replacement of the stockpile of topsoil to the mined area, reseeding, and mulching necessary to re-establish vegetative cover for permanent slope stabilization and erosion control, provided also that the minimum depth of topsoil shall not be less than six (6) inches after reclamation. No restored slopes may exceed the gradients shown on Interim Reclamation Plan. Y. No mining activity will occur within fifteen (15) vertical feet of bedrock. Z. Dakota Aggregates shall compact the entire reclamation site to a minimum compaction of 95% of maximum dry density. AA. If not utilized by the University of Minnesota for agricultural purposes, fully reclaimed areas will be permanently seeded within 14 days of final completion. All disturbed non-operating areas not utilized by the University of Minnesota for agricultural purposes shall be seeded at a minimum of once per year, prior to October 1 with MnDOT seed mix 130B. Operating areas including work faces, material stockpiles, haul roads, staging areas, and active reclamation areas are not required to be seeded. BB. Dakota Aggregates shall submit quarterly to the City documentation of the Barr Engineering, Inc. (or other City approved geotechnical testing firm) environmental and geotechnical testing with documentation verifying the source and quantity of the “haul-back” material. These reports shall be provided within fourteen (14) days after the end of the quarter. CC. Dakota Aggregates shall submit an incidence report to the City within three days of any testing that fails for contamination or hazardous materials, or will not produce a normal moisture-density relationship for compaction. DD. Truck operators within the pit area shall not engage in practices involving slamming tailgates, vibrating boxes, using of “jake” or engine brakes (except in emergency situations), or other such activities that result in excessive noise. EE. Dakota Aggregates shall incorporate best management practices for controlling dust, erosion, noise, and storm water runoff as specified by the Minnesota Pollution Control Agency and the United States Environmental Protection Agency and proposed in the submitted LSME application to the City. FF. Compliance with Dakota County Ordinances No. 110 and 111, as well as all other applicable Federal, Minnesota, Dakota County, and Rosemount regulations. Soil materials in the Property will be managed in accordance with the Minnesota Pollution Control Agency’s Best Management Practices (BMPS) for the Off-Site Reuse of Unregulated Fill. 20165 Annual Operating Permit Dakota Aggregates, LLC 5 of 5 GG. Dakota Aggregates may not assign this permit without written approval of the City. Dakota Aggregates will be responsible for all requirements of this permit and all City ordinances on the licensed premises for the permit period unless Dakota Aggregates gives sixty (60) days prior written notice to the City of termination and surrenders permit to the City. Dakota Aggregates shall identify all Operators prior to their commencement of mineral extraction-related activities in the pit area. The City shall have the authority to cause all mineral extraction activities to cease at any time there is an apparent breach of the terms of this Permit. HH. Dakota Aggregates shall comply with such other requirements of the City Council as it shall from time to time deem proper and necessary for the protection of the citizens and general welfare of the community. II. Dakota Aggregates shall install and establish vegetation on a berm located on the north side of the haul road by the review of the 2016 annual permit. The construction of this berm to its westernmost end point at Biscayne Avenue shall be completed by June 30, 2016. JJ. American Engineering Testing, Inc. (AET) shall revise submit the 20143-20154 Annual Monitoring Report to , includinge the November 2014all groundwater testing, and submit the revised report to the City by January 31, 20165. Leggette, Brashears, & Graham, Inc. (LBG) shall review the revised report on behalf of the City and has the authority to reduce adjust the frequency of the groundwater sampling to semi-annual based on the 2015 testing results. of the November 2014 testing results. JJ.KK. Dakota Aggregates shall implement the sound mitigation measures as documented in its 2016 Large Scale Mineral Extraction Permit application and referenced in the March 1, 2016 City Council report concerning said application. IN WITNESS WHEREOF, Dakota Aggregates, LLC, the Operator, hereby consents and agrees to the foregoing conditions of said Annual Operating Permit this _______ day of ______________, 20__. Dakota Aggregates, LLC By:________________________________ Tim Becken, Its Chief Manager STATE OF MINNESOTA ) ) ss 20165 Annual Operating Permit Dakota Aggregates, LLC 6 of 5 COUNTY OF _________ ) The foregoing instrument was acknowledged before me this _________ day of ____________, 20____, by Tim Becken, Chief Manager of Dakota Aggregates, LLC, the Operator, on behalf of the Corporation. ________________________________________ Notary Public January 20, 2016 City of Rosemount Planning Commission 2875 145th Street West Rosemount MN 55068 RE: Public Hearing regarding 24 hour operation of aggregate processing facility Dear Planning Commission: ou den the application b DakotaAsaresidentofRosemount, we respectfully request that y y pp y Aggregates, LLC, to amend the Interim Use Permit to allow 24 hour operation of the aggregate processing facility in Rosemount. We have lived at 14412 Bentley Way since November, 1999. We were the first single family home to close in the Bloomfield development so we have obviously witnessed a lot of growth and change in Rosemount and UMore. We are already forced to deal with noise and lights from the aggregate operation today. The lights are very powerful and are clearly visible from our back windows and deck of our home. Activity at the aggregate facility will no doubt pick up when warmer weather arrives as will our desire to be outside enjoying our yard and deck. We don't wish to be subjected to additional activity at all hours. Summer evenings and weekends are precious commodities in Minnesota and we would like to enjoy the home that we love without the side effects of a commercial gravel operation in sight and hearing distance of our home. Sincerely, Peter and Martha Jane Magnuson Home phone: 651-322-7922 Cell phone: 651-747-6072 (Martha) or 651-747-6073 (Peter) Email: mjmagl2(q vahoo.com or pd.magnusonlLgmail..com January 26, 2016 Rosemount Planning Commission: 2875 145th Street West Rosemount,MN 55068 RE: Dakota Aggregate Mine 24 hour Operation Rosemount MN We are writing you because we cannot attend the planning commission meeting reference the 24 hour proposed operations. I and my wife are adamantly against Dakota Aggregate operating 24 hours a day, We live on Bloomfield Place and our back yard/home faces the south and the operating mine. The reasons: Mining noise that is very loud, disruptive and keeps us both awake a night Bright obnoxious lights Dust 24/7 if wind conditions are right—dirt and dust come right into our home(except winter when we have our windows closed) Our widows and siding are covered with the dirt and dust from the mining operations This mine will effect resale of our home,especially if 24 hour operations You, as the planning commission should seriously take into consideration and adamantly oppose Dakota Aggregate from operating 24 hours a day. This 24 hour operation of the mine is an interruption of our lives with the noise as well as hundreds of other people's lives. It's bad enough that we have to live with the noise, lights and dust during the daytime hours. I am curious if any of planning commission lives in earshot/light shot or dust shot of the mine? You as the planning commission must remember, we were here first. When we purchased and built this home I had no idea there would be a noisy disruptive aggregate mine across the street. If we would have known this, we would not have moved to Rosemount. Please help us and others that live near the aggregate mine and Vote NO. Please submit this letter during the planning commission meeting on January 26, 2016, as well as on file with the city of Rosemount. Regards, Bobby and Julie Reardon 14554 Bloom field Place ffeardon@charter.net Roudebush, Amy From: Roudebush, Amy Sent: Monday,January 25, 2016 3:19 PM To: Forster, Ryan'; 'Freeman, Gretchen'; 'Henrie, Brandon'; 'Kurle,Joseph'; Lindquist, Kim; Melissa Kenninger(mkenninger@gmail.com)'; 'Miller,Wade'; 'Pam VanderWiel' Subject: FW: oppose the working of the Aggregate Company 24/7 One more resident complaint to add for Dakota Agg's renewal for tomorrow's meeting. Amy Roudebush, Planning & Personnel Secretary City of Rosemount,2875 145th Street W,Rosemount,MN 55068 Ph.651-322-2051h/hhttp://www.ci.rose mount.mn.us ROSEC V OU From: CINDY CURLEY Imailto:curlette@msn.coml Sent:Thursday, January 21, 2016 6:14 PM To:Comment<Comment@ci.rosemount.mn.us> Subject:oppose the working of the Aggregate Company 24/7 1 can not make the meeting on January 26th, but I wanted you to know that I vehemently oppose the Aggregate Company running their business round the clock...how thoughtless, greedy and self serving can you get!! The main reason many of us have moved and lived in Rosemount is because of it's relative small town feel along with the peace and quiet! Please don't allow this company to strip of us peace and quiet along with destroying the land! With regards, Cindy Curley 14834 Bittersweet Circle Rosemount, MN 55068 1 G¸WX BA N Y A N TH S T W ( C S A H 4 2 ) BI S C A Y N E A V E BI S C A Y N E A V E B I T T E R - S W E E T C T BI T T E R -S W E E T CI R BLOOOM F I E L D WAY A U G U S TAWAY STAT I O N T R L BR A Z I L A V E BLOOOMFIELDPL BLOOMFIEL D CIR 148TH ST W BL A N C A A V E BOULDER TRL BL O O M F I E L D BELFAST ST W BOX W O O D P A T H BEECH ST W A Z A L E A B AY B E R R Y T R L 160TH ST W (CSAH 46) B US I NE SS PK W Y BAYBERRY BOYSENBERRY CT BLACKBERRY 150 151ST CT W AT W O O D CI R PAT H BLOOMF I E L D B L U E B E R R Y C T C T B I S C A Y N E W A Y B A Y B E R R Y A UDOBA N W A Y TRL BRENNER CT BOSTONCIR ATWOOD CT142NDST W CIRCTWAY B E L L E C T 142NDCT W W A Y B L O O M F I ELDPATH A T W ATER WAY CT LN B E N T L E Y BOISECIR A U B U R N A V E AZALEA P A T H 160TH ST W (CSAH 46) 145TH ST W AURORA AVE L 147THCT 149TH ST W A L L I N G H A M A V E AL D B O R O U G H AV E ALMA CI R G¸WX BA N Y A N TH S T W ( C S A H 4 2 ) BI S C A Y N E A V E BI S C A Y N E A V E B I T T E R - S W E E T C T BI T T E R -S W E E T CI R BLOOOM F I E L D WAY A U G U S TAWAY STAT I O N T R L BR A Z I L A V E BLOOOMFIELDPL BLOOMFIEL D CIR 148TH ST W BL A N C A A V E BOULDER TRL BL O O M F I E L D BELFAST ST W BOX W O O D P A T H BEECH ST W A Z A L E A B AY B E R R Y T R L 160TH ST W (CSAH 46) B US I NE SS PK W Y BAYBERRY BOYSENBERRY CT BLACKBERRY 150 151ST CT W AT W O O D CI R PAT H BLOOMF I E L D B L U E B E R R Y C T C T B I S C A Y N E W A Y B A Y B E R R Y A UDOBA N W A Y TRL BRENNER CT BOSTONCIR ATWOOD CT142NDST W CIRCTWAY B E L L E C T 142NDCT W W A Y B L O O M F I ELDPATH A T W ATER WAY CT LN B E N T L E Y BOISECIR A U B U R N A V E AZALEA P A T H 160TH ST W (CSAH 46) 145TH ST W AURORA AVE L 147THCT 149TH ST W A L L I N G H A M A V E AL D B O R O U G H AV E ALMA CI R P a t h : T : \ G I S \ C i t y \ M a p s \ D e p a r t m e n t a l M a p s \ C o m m u n i t y D e v e l o p m e n t \ M i n i n g \ M i n i n g C o m m e n t s . m x d Opposing 24 hr Mining at Dakota Aggregates Residents Mining Area Phase 1 Mining Area Phase 1 & 2 BU F F E R Table of Contents 1) Permit Application/ Narrative/ Plan Set Sound Monitoring/Mitigation by Aeroacoustics Engineering Consultants, LLC: 2) Acoustic & Noise Guidelines 3) Site Acoustic Testing&Summary 4) Engineered Noise Mitigation Examples 5) 2015 3-D Acoustic Model 6) 2016 3-D Acoustic Model 7) Onsite Nighttime Acoustic Testing Results November 2nd & 3rd, 2015 8) 2015 Sound Mitigation /Complaint Log UMore Park Large Scale Non Metallic Mineral Extraction Annual Operating Permit Application Proposed Dry Mining Phases 2A/2B/1C Active North Dry Mining Phases lA/1B/2C/2D & Active Wet/Dry Phases IA-2B UMore Park City of Rosemount December 15, 2015 1. Land Owner: Regents of the University of Minnesota UMore Development LLC 1300 South 2'Street, Suite 208 Minneapolis,MN 55455 2. Applicant/Operator: Dakota Aggregates,LLC 2025 Centre Pointe Boulevard, Suite 300 Mendota Heights,MN 55120 651)688-9292 3. Legal Description of the Land upon which Excavation is active: That part South Half of Section 28,Township 115,Range 19,Dakota County,Minnesota,lying westerly of the following described line; Commencing at the northeast corner of the Southeast Quarter of said Section 28;thence South 89 degrees 48 minutes 43 seconds West,assumed bearing along the north line of said Southeast uarter,a distance of 1058.90 feet to the point of beginning of the line to be described; thenceQpgg West a distance 1211.64 feet;thence South 07South18degrees23minutes48secondsW degrees 11 minutes 26 seconds East a distance of 1472.46 feet; thence South 75 degrees 07 minutes 52 seconds East a distance of 126.03 feet to the south line of said Southeast Quarter and there terminating. EXCEPT the plat of UNIVERSITY ADDITION, said Dakota County. AND Section 33,Township 115,Range 19,Dakota County,Minnesota;EXCEPT the East 133.00 feet of the North 549.43 feet of the Southeast Quarter of said Section 33; EXCEPT the East 133.00 feet of the South 930.25 feet of the Northeast Quarter of said Section 33; also EXCEPT that part of said Northeast Quarter described as follows: Beginning at the northeast corner of said Northeast Quarter;thence South 00 degrees 11 minutes 58 seconds West, assumed bearing along the East line of said Northwest Quarter,a distance of 800.63 feet;thence North 81 degrees 23 minutes 25 seconds West a distance of 40.76 feet; thence North 38 degrees 17 minutes 54 seconds West a distance of 819.06 feet;thence North 75 degrees 07 minutes to the north line of said Northwest Quarter; thence North52secondsWestadistanceof580.25 feet 89 degrees 51 seconds 14 seconds East, along said north line,a distance of 1111.53 feet to the point of beginning. 1 AND That part of the Northwest Quarter of Section 34,Township 115,Range 19,Dakota County, Minnesota,described as follows: Commencing at the northwest corner of said Northwest Quarter;thence South 00 degrees 11 minutes 58 seconds West,assumed bearing along the west line of said Northwest Quarter,a distance of 800.63 feet to the point of beginning of the land to be described;thence continuing South 00 degrees 11 minutes 58 seconds West, along said west line,a distance of 912.75 feet; thence North 89 degrees 51 minutes 14 seconds East a distance of 647.18 feet; thence North 00 degrees 11 minutes 58 seconds East a distance of 813.16 feet;thence North 81 degrees 23 minutes 25 seconds West a distance of 654.21 feet to the point of beginning. AND That part of the Southwest Quarter of Section 34,Township 115,Range 19,Dakota County, Minnesota,lying southerly of the following described line: Commencing at the northwest corner of said Southwest Quarter;thence South 00 degrees 11 minutes 58 seconds West, assumed bearing along the west line of said Southwest Quarter,a distance of 549.45 feet to the point of beginning of the line to be described;thence South 89 degrees 28 minutes 53 seconds East a distance of 2646.92 feet to the east line of said Southwest Quarter and there terminating And lying westerly, northwesterly and northerly of the following described line: Commencing at the southwest corner of said Southwest Quarter;thence South 89 degrees 42 minutes 10 seconds East,along the south line of said Southwest Quarter,a distance of 2192.17 feet to the point of beginning of the line to be described; thence North 04 degrees 21 seconds 18 seconds East a distance of 142.12 feet;thence North 01 degrees 12 minutes 32 seconds West a distance of 368.88 feet; thence North 01 degrees 58 minutes 09 seconds West a distance of 266.72 feet;thence northeasterly 194.60 feet,along tangential curve,concave to the southeast,having a central angle of 96 degrees 57 minutes 13 seconds and a radius of 115.00 feet;thence South 85 degrees 00 minutes 56 seconds East,tangent to last described curve,a distance of 157.25 feet; thence easterly 99.70 feet,along a tangential curve, concave to the north, having a central angle of 09 degrees 25 minutes 45 seconds and a radius of 605.84 feet;thence northeasterly 100.73 feet, along a reverse curve,concave to the northwest,having a central angle of 56 degrees 01 minutes 50 seconds and a radius of 103.00 feet to the west line of said Southwest Quarter and said line there terminating. 2 North Dry Mining Phases 1A- 1C 2A-2D Annual Review U date Activities related to North Dry Mining will continue to include relocation of surface soils for construction of the+/-20 foot tall north mine berm,mixing and screening, stockpiling, loading, hauling and conveying of aggregate material to the Ancillary Use Facility(AUT)or hauled out by use of the Akron Avenue internal/rail bed corridor. All rock from the North Dry Mining operation is conveyed south to the processing facility for material production. The North processing equipment has been lowered approximately 50 feet into the North pit floor. In addition a 20+/-berm is being constructed on the north side of the permitted North Dry Mining phases over to the northwest corner of Dry Mining Phase 7A(up to Biscayne Avenue)which will be finished in spring/summer of 2016. North Dry Mining Phases: Sub phase IA: active mining 07.68 Acres) Sub phase 1B: active mining 10.05 Acres) Sub phase 1C: proposed to be opened in 2016 12.57 Acres) Sub phase 2A: proposed to be opened in 2016 6.82 Acres) Sub phase 2B: proposed to be opened in 2016 8.74 Acres) Sub phase 2C: active mining 09.17Acres) Sub phase 21): active mining 08.12Acres) Total Acres North Dry Mining: 63.15 Acres) Aggregate Material sold from January 1,2015-October 31,2015: 85,000 Tons Aggregate stockpiles onsite as of October 31, 2015 in North Dry Mining Area Sand: 288,000 TONS All rock is conveyed to the aggregate processing facility for mixing and production of various aggregate products. Dry/Wet Mining Sub-Phase IA-2B Annual Review Update: Activities in the Dry/Wet mining phases will continue to include relocation of surface soils on the remaining 10+/-acres of virgin ground,crushing,mixing, screening, stockpiling, aggregate washing, loading, any conveying of material to the AUF. Once the material is conveyed to the AUF,it will be processed into varying grades of aggregate products that will be purchased and hauled offsite utilizing the Station Trail/CSAH#46 access. The screening berm landscaped with trees which is adjacent to County Road 46 and to Wet Dry Mining Phases lA and 2A has been maintained throughout the season including replacement of approximately 20 dead trees. Dry/Wet Mining Phases: Sub phase IA: active mining 25.32 Acres) Sub phase 1B: active mining 18.21 Acres) Sub phase 2A: active except for approx.4 acres to be opened 17.03 Acres) Sub phase 2B: active except for approx. 6 acres to be opened 17.90 Acres) Total Acres Dry/Wet Mining: 78.46 Acres) 3 Aggregate material sold from January 1,2015-October 31,2015: 1,038,000 Tons Aggregate Stockpiles in Aggregate Processing Facility as of October 31,2015 Screened Sand: 75,200 TONS Washed Sand: 224,100 TONS 3/8" washed rock: 9,900 TONS 67 washed rock: 31,500 TONS 1 ''/2" washed rock: 5,100 TONS Class 5:30,300 TONS 1 ''/z' crushed rock: 18,000 TONS 3/" screened/crushed rock: 6,800 TONS Recycled Aggregate: RAP Sold January 1,2015—October 31,2015: 41,300 TONS RAP Stockpile January 1,2015 —October 31,2015: 21,700 TONS Site Improvements Update: Over$50,000,000.00 (Fifty Million Dollars)in onsite improvements since inception of the project in 2013 Hardrives Bituminous plant up and running for the start of the 2015 construction season Cemstone Products Company ready mixed concrete plant opened in December of 2015. Over 300 acres(AUF and active mine areas) has been added to the tax roll since 2013 Maintenance of existing trees situated on the berm abutting CSAH#46 including replacement of approximately 20 trees which were a victim of winter burn Berm,ditch and common areas maintained routinely throughout the year. Continuation of berm construction on the north side of the permitted North Dry mining phases to be constructed to the Northwest corner of Dry Mining Phase 7A(up to Biscayne Avenue)to completed in spring/summer of 2016 Relocate/lower north end mining equipment into the north mine floor 70 feet in depth. (pit floor is 50 feet down and north berm is 20 feet in height) Completed the concrete curb and gutter and roadway pavement section on 158'Street and Station Trail. Sign Erection at Akron Avenue and County Road#46 in 2016 4 Sign installation at County Road#46 and Station Trail Complete. 50 foot ornamental and power operated gate installed at Akron Avenue 50 foot custom gate on North Haul Road at Akron 5 44R Rosemount City Hall 2875 145TH Street West Rosemount, MN 55068 COMMUNITY.DEVELOPMENT 651-423-4411 651-423-4424 (FA) revised 02.29.12 LARGE SCALE MINERAL EXTRACTION PERMIT APPLICATION Aicant ANNUAL REVIEW Name:._ Dakota Aggregates, LLC Address:2025 Centre Pointe Blvd., Ste 300 Mendota:Heights,MN 55120 Email Address: patmason@amesco.com Property Owner Name: Regents of the University of Minnesota Address: 230 McNamara Alumni Center,200 Oak Street S.E.Minneapolis, MN 55455 Person/Corporation Conducting Extraction Name: Dakota Aggregates, LLC Address: 2025 Centre Pointe Blvd.,Ste 300 Mendota Heights, MN 55120 Purpose of Excavation/Extraction:(Describe in Detail) Attached. Property Information/Excavation Site Legal Description: Attached. DryMet mining phases(1 A, 113,2A,213)78.46 Acres North Dry Mining(1A-1 C&2A-2D)63.15 Acres. include PID#) 34-03310-01-010 &34-02810-50-091 TOTAL ACREAGE: North Dry Mining (63.15 Acres)Wet/Dry Mining 78.46 Acres Type of Material to be Extracted: Constructing grade sand and gravel Total Cubic Yards to be Extracted: North dry mining 3,324,000 Tons/Wet/Dry Mining 5,300,000 Tons Estimated Number of Years of Operation: 3-5 years North Dry Mining&4-5 years Wet/Dry Mining Estimated Date for Completion of Site Rehabilitation: Prior to extraction belna authorized, s no more than 160 Acres AccessRransport Routes: Name of highways, streets or other public roadways within the City upon which the material will be transported) Required Attachments L^_J Phasing Plan 0 Site Reclamation and Rehabilitation Plan MV Names and Addresses of adjacent land owners within 250 feet of extraction site 0 Map showing physical relationship of excavation site to the community and existing community development 0 Site analysis information (trees, depth of topsoil, adjacent on-site structures and land uses,flood levels,watercourses and elevation and percent slope within 100 feet beyond site perimeter 0 Depth of watertables throughout excavation site Plan of Operation Drainage,Wind and Water Erosion Control Plan This application must be accompanied by a list of names and addresses of property owners within a 350 foot radius of the subject property or, if application pertains to property located in Agricultural(AG), Agricultural Preserve (AP), or Rural Residential(RR)District, the application must be accompanied by a list ofnames and addresses of property owners within a quarter 1/4)mile. Also to be included are two sets of address labels of the property owners. These must accompany the application at the time of submittal. This permit,upon authorization by City Council, is valid from January 1 through December 31 of the year of issuance. The proposed mineral extraction will be reviewed according to submitted plans and description of the proposed operation as required under provisions detained in City of Rosemount Zoning Ordinance, Section I Z 4 Mineral Extraction. In submitting this application the applicant recognized.the requirements set forth in-the City of Rosemount-Ordinance for the regulation of mining and agrees to meet those conditions prior to.requesting approval of this permit BY CHECKING THIS BOX, I HEREBY AGREE TO ALL STATEMENTS HEREIN AND SUBMIT MY SIGNATURE ELECTRONICALLY TO THIS FORM. 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WO - 6 l+ d 4 I V) t r.__.. d- ` W m Z W C Q U ( 1... i Q n N Ifry n L_ L_ n 9Z6 Q 0 O O V 11!< Nr7 w JJ r N NN U) o d- N 000 Q cn j/ 1r ov r CD ULi 0 W C)QQ Ln0 Ln m f C o m CN DD oQD 1,- Ile, CD Ld d Vi 9 i AA 18 January 2016 E-mail: lany.hansen@aecnonoise.com Direct Dial: 763-546-8565 Dakota Aggregates, LLC. 2025 Centre Point Blvd. /Suite#300 Mendota Heights, MN 55120 Attention: Mr. Stacey Hannover, Production Manager Subject: Summary/clarification of noise mitigation project graphics and data for the forth coming Rosemount Council meeting. Reference: 1. DAL Purchase Order#551-1656. 2. AEC Project#JE01-9406. Dear Mr. Hannover: Pursuant to your request, we have assembled a selection of data and graphics to describe the Aeroacoustic Engineering Consultants, LLC (AEC) work scope, progress and findings for our joint noise mitigation project for Dakota Aggregates, LLC (DAL). To date, North property line environmental acoustic testing has been initiated and at least one (1) engineering control has been scheduled to reduce noise propagation to desirable limits. This document is a rudimentary explanation of project issues and findings: Acoustic& Noise Guidelines First graphic depicts a sound thermometer displaying the range of perceived sound from the threshold of human hearing through the threshold of pain. The unit of sound measure is the decibel (dB) and is numerically presented along the thermometer's right side, with various activities associated with noise/sound intensities. For our DAL criteria, we are looking at a maximum noise range from a living room" to"conversational speech," or a nominal 50-dB level of intensity. It should be noted, a t3-dBA change is seldom noticed but a *5-dBA change is clearly noticeable. Site Acoustic Testing&Summary First graphic is an aerial map which depicts an overview of two(2) initial environmental acoustic test locations, general North and East residential areas and adjacent quarry operation to DAL. Second graphic depicts the typical instrumentation deployment for sound and climatic instrumentation at each test point location. Third graphic is a summary of Minnesota Pollution Control Agency (MPGA) criteria for residential land use, sound data from both test locations and stop time for both quarry operations. An Lio s 55-dBA limit means the measured sound pressure level (SPL) shall not exceed 55-dBA for more than 6-minutes of any 1-hour test period. An L50:5 50-dBA limit means Continued . . . AEROACOUSTIC ENGINEERING CONSULTANTS,LLC 8014 Olson Highway/#210, Minneapolis, MN 55427-4712 United States of America website:www.aecnonoise.com Dakota Aggregates, LLC. 18 January 2016 Page 2 of 3 the measured SPL shall not exceed 50-dBA for more than 30-minutes of any 1-hour test period. Acoustic test data is grouped by individual test dates of 02 and 03 November 2015 and in hourly 1-hour) line item time periods. L,o and L50 dBA levels are color coded: red for exceeds limits and green for within limits. CR-42 (I Se Street West) traffic dominated the 02 November and approximately 50% of 03 November 2015 acoustic measurements. With the reduced traffic flow on 03 November 2015, the quant' noise appears to be contributing approximately 3-dBA to the over limit of the L,a maximum of 55-dBA for 11:00-pm to 12:01-am. Enaineered Noise Mitigation Examples First graphic depicts a recent engineering control project to remediate an acoustic event reported by a private resident. The concern was the abrupt and intense noise generated by equipment start-up alarms mandated by safety regulations. A new alarm was found that complied with site safety code and reduced audible noise from 96-dBA to 77.8-dBA. This is a noise reduction of nearly 20-dBA and given the distance from the private residence, should reduce resident sound below perceptible levels. "Background' is the ambient SPL with both alarms off. 2015. 3-0 Acoustic Model This data group is AEC 3-D acoustic computer modeling of area noise contours based on DAL equipment locations, calculated screening noise emissions and berm length during the 2015 quarry operation. Its primary intent is to establish a reference base for comparison to proposed changes in the 2016 quarry operation: First graphic, the AEC computer model virtually shut off all quarry activity and depicts only the 2015/2016 traffic flow noise generated on CR-42 (1500'Street West). Second graphic, the AEC computer model virtually shut off all traffic flow noise from CR-42 150Street West)and depicts only the estimated screen noise generated at the 2015 location. Third graphic, the AEC computer model combines 2015/2016 traffic flow noise from CR-42 150'hStreet West) and the estimated screen noise generated at the 2015 location. 2016. 3-D Acoustic Model This data group is AEC 3-13 acoustic computer modeling of area noise contours based on DAL equipment locations in new 507foot deep pit, extended berm tenth. and calculated screening noise emissions for the 2016 quarry operation. Its primary intent is to evaluate revised noise emission patterns by comparison to 2015 quarry operation: First graphic, the AEC computer model virtually shut off all quarry activity and depicts only the Continued . . . Environmental Engineering Aerodynamics/Thermodynamics Industrial Noise & Vibration Control Analysis/Diagnostics/Remediation Dakota Aggregates, LLC. 18 January 2016 Page 3 of 3 2015/2016 traffic flow noise generated on CR-42(150d'Street West). This is identical to the first graphic in the 2015 simulation set. Second graphic, the AEC computer model virtually shut off all traffic flow noise from CR-42 150' Street West) and depicts only the estimated screen noise generated at the 2016 location. The changes in depicted acoustic emission patterns are attributable to the relocation of equipment to a 50-foot deep pit and the net effect of a nominal 70-foot acoustic barrier(50-foot deep pit + 20-foot high berm). The acoustic lobe protruding toward the Northwest residential area is an artifact of a temporary void (equipment access ramp) between the old berm and the new berm extension; this lobe will contract toward the Southeast when the berms are connected. Thi, graphic, the AEC computer model combines 2015/2016 traffic flow noise from CR-42 150 Street West)and the estimated screen noise generated at the 2016 location. Deductions: 1. All processing equipment relocated in the new, 2016 pit location should exhibit a nominal 5-dBA reduction in noise beyond the DAL North and East property lines. 2. Any unusual acoustic events similar to the equipment start-up alarms, will be remediated by engineering controls which generally yield much larger noise reductions. 3. Prompt and ongoing acoustic diligence should maintain DAL quant' activities well within MPCA noise criteria for private residence areas, beyond their property lines. As discussed, AEC can have an engineer available during the council meeting to address any technical questions. Thank you for the opportunity to be of service! Respectfully yours, Aeroacousti nnginee ' g Consultants, LLC Lawrence F. Hansen—Principal Engineer Enclosures: File:Ur DAL Council 5ummary.doc Environmental Engineering Aerodynamics/Thermodynamics Industrial Noise 8 Vibration Control Analysis/Diagnostics/Remediation STATEMENT OF QUALIFICATIONS FOR AEROACOUSTIC ENGINEERING CONSULTANTS, LLC. Facilities • Personnel • Qualifications • Services • Aeroacoustic Engineering Consultants, LLC. (AEC) has an extensive background in acoustic / aerodynamic /vibration diagnostics and sound suppression systems. AEC was selected to design and build hybrid, reactive silencers for the life support system onboard the NASA Space Shuttle as well as the solid fuel processors for the booster rockets! Conversely, AEC expertise was utilized in the development of deep-dive technology (-20 dBA hydro space)for naval vessels, marine salvage and oceanographic exploration. For military and commercial Wind Tunnels, AEC is repeatedly tasked for analytical design, computer simulation, fabrication and testing of all aeroacoustic systems for low-Mach through hypersonic flows, including the U.S. Navy's next generation, ultrahigh Mach Railgun. AEC furnished design & build for professional, digital recording and dubbing studios. Our analysis and acoustic testing have been the foundation for performing arts' theater design, world wide. AEC was commissioned to provide acoustic/vibration analysis, design and testing services for the new JFK International Air Terminal #4 in New York, including Concord (SST) operations. The Army Corp of Engineers has utilized AEC expertize for acoustic and seismic silencing of an energy material forensics test facility that detonates explosive devices up to and including small nuclear weapons. Industrial and government entities such as Microsoft, U.S. Central Intelligence Agency (CIA) and the National Geospatial-Intelligence Agency NGA) have employed AEC's aeroacoustic skills for diagnostics, design and/or remediation of very large scale, highly secured data system facilities. At the request of state and federal compliance officers, AEC has conducted seminars for OSHA, MSHA Mine Safety and Health Agency, formally MESHA) and corporate compliance officers for noise control methodology in surface, open pit and subsurface mining. For reference, a cursory outline of the product and engineering support AEC can offer has been incorporated, below. SYSTEM CONSULTATION, PROJECT DEFINITION AND MANAGEMENT" AEC's principal forte is the control of environmental, industrial, architectural, aerodynamic and mechanical system noise/vibration. Our engineers utilize current, state-of-art instrumentation and recorders (ANSI/ISO calibration standards) for problem analysis and solution (compliance) certification. An integral part of our engineering program is the concept of computerized predictive acoustic modeling, computational fluid dynamics (CFD) for volume/mass flow analysis and computer aided design. AEC computer models have been repeatedly tested and validated in scores of critical systems including large scale aerospace structures, submarine applications and high reliability telecommunication and data storage facilities. Continued . . . . . Statement of Qualifications Aeroacoustic Engineering Consultants, LLC. Page 2 of 3 These 3-dimensional computer models allow AEC to analyze hundreds of material array's and/or subsystems, digitally synthesize their implementation and accurately predict their performance. Thoughtful integration of computer aided analysis, design, scheduling and manufacturing will provide a substantial reduction in project expenses. SYSTEM DESIGN** Engineering is supported by a design department consisting of senior designers and draftsmen. Together, our aeroacoustic engineers and design group will generate complete specifications, conceptual illustrations and/or 3-dimensional AutoCAD design drawings to meet the acoustical, physical, thermodynamic and aerodynamic criteria. Due to AEC's intimate knowledge of equipment manufacturing, clients can be assured of practical designs which may be economically implemented. ACOUSTIC TESTING, AERODYNAMICS/THERMODYNAMICS and VIBRATION ANALYSIS for IN SITU and/or LABORATORY ENVIRONMENTS AEC maintains strict calibration on a wide variety of aerodynamic analysis, sound measuring, vibration and meteorological testing/monitoring instrumentation. These portable systems are utilized in prototype testing, field analysis and in situ certification. Portable, real-time frequency analyzer system can accommodate a microphone spread more than 250 feet and datalog complete spectrum/intensities from 0.7 Hz to 22,400 Hz at +/- 0.1 dB tolerance every 0.001 seconds. Dedicated computer system supports fast Fourier transforms (FFT) / time correlation for acoustic and vibration measurement and analysis. Forced vibration system provides empirical data on intrinsic impact/vibration isolation capabilities of any building or structure. Aerodynamic tests are accomplished in a computer controlled, open circuit, low-Mach wind tunnel for turbulent or laminar flows. AEC's commitment to system analysis extends to the maintenance of a portable Aerodynamic Diagnostics Laboratory, complete with flow visualization capabilities and analytic instrumentation. The Aero Lab is an essential element in product and system testing for compatibility with the clients' environmental requirements, CFD computer model calibration/verification and long term system stability and reliability. FABRICATION/INSTALLATION** Supplementing AEC system engineering are manufacturing facilities skilled in the fabrication of noise control products and systems. Computer controlled, resistance welders are gimbaled for 3-axis mobility with temperature controlled, closed circuit, cooling achieving repeatable weld quality. High performance panels and airfoil forms are an amalgam of acoustical media in a proprietary, lamination process. Situated in key geographic locations, manufactured aeroacoustic systems may be shipped quickly to client's designated regional site. Continued . . . . . Statement of Qualifications Aeroacoustic Engineering Consultants, LLC. Page 3 of 3 From structural steel weldments to sheet metal fabrication to high performance complex acoustical elements, AEC can provide a single source for all project requirements. Staffed with skilled craftsmen, each facility can accommodate prototypes as well as production runs. AEC also fields a staff of qualified, installation experts who assume total installation responsibility or provide consultation to in-plant/site personnel. The AEC Total Quality Management System meets or exceeds MIL-Q-9858 (as required). From project engineering and/or conceptual designs through system manufacturing to installation, AEC will provide any portion or supply a "turnkey responsibility." For more detailed background information on AEC diagnostics, systems and engineering services, visit the AEC web site at: www,aecnonoise.com. Also included on the AEC web site is a "Gallery" of photographs of a few, select highlights from over 44-years of practice in the discipline of aeroacoustics, aerodynamics, noise control and vibration/shock analysis. As noted, AEC will also provide system analysis, consulting engineering, acoustic/vibration testing and acoustical hardware for high noise and/or critical use spaces in architectural buildings or structures. Existing buildings can be empirically tested for acoustic and vibration containment capabilities and new structures may be computer modeled to assure proposed construction will meet acoustic and vibration criteria. AEROACOUSTIC ENGINEERING CONSULTANTS, LLC. 8014 Olson Highway/#210 Minneapolis, Minnesota 55427-4712; United States of America Telephone: 763-355-2030 Time Zone: -0600 UTC/GMT; Central (USA) Web Site: www.aecnonoise.com 1972 - 2016: OVER 44 YEARS OF AEROACOUSTIC SOLUTIONS file:AEC Stmnt Qualif Acoustic.doc AEROACOUSTICS ENGINEERING CONSULTANTS, LLC. 8014 Olson Highway / #210 Minneapolis, Minnesota 55427-4712; United States of America Time Zone: -0600 UTC/GMT; Central (USA) Telephone: 763-355-2030 Web Site: www.aecnonoise.com file:Cover Acoustic&Noise Guidelines.doc II r •, A MY IML ML. Iv I Aw- II iw AA a i c A11111111 No Mill NIIINIF ItiFp 111iiilliii; '! it % iii IIiIIH;11 f•i Mif IM::N (;INIr I INIi`dNil Ni1i 1 U11IM1111% OEM% ?'A ANM11'1111 III IAP'. 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R. 7030.0040: Daytime (7:00-am to 10:00-pm): L10 :5 65-dBA; L50 :5 60-dBA Nighttime (10:00-pm — 7:00-am): 1-105 55-dBA; L50 :5 50-dBA Monday 02 November 2015 Acoustic Test Measurements @ TP-2 ( CR-42 / 150th Street West, approximately 1200-yards East of Biscayne Avenue): Nighttime (10:00-pm — 11:00-pm): 1-10 :5 65.5-dBA; L50 :5 55.6-dBA Nighttime (11:00-pm — 12:01-am): 1-10 <_ 62.2-dBA; 1-50 <_ 52.3-dBA Nighttime (12:01-am — 1:00-am): L10 S 56.9-dBA; L50 <_46.6-dBA Nighttime (1:00-am — 2:00-am): L10 :5 56.7-dBA; L505 42.7-dBA Note: Traffic noise dominated during 10:00-pm to 1:00-am segments. Tuesday 03 November 2015 Acoustic Test Measurements @ TP-1 (CR-42 and Biscayne Avenue,just South of CR-42 on Biscayne Avenue): Nighttime (10:00-pm — 11:00-pm): L,0 !5 59.6-dBA; L50 :5 50.6-dBA Nighttime (11:00-pm — 12:01-am): L10 <_ 57.3-dBA; L50 <_47.6-dBA Nighttime (12:01-am — 1:00-am): 1-10 <_ 54.4-dBA; L50 <_41.1-dBA Nighttime (1:00-am — 2:00-am): L10 :5 51.4-dBA; L50 :5 37 9-dBA Dakota Aggregate work stop time (confirmed): 11:59-pm Aggregate Industries (unconfirmed): 2:00-am Aggregate Ind. located in S.W. quadrant of Biscayne & 160th, Empire Township] File: DAL JE9406 1-hr Summary.doc AEROACOUSTICS ENGINEERING CONSU_TANTS 'LC:` 8014 Olson Highway / #210 Minneapolis, Minnesota 55427-4712; United :Mates of Amerid Time Zone: -0500 UTC/GMT; Central (USA) Telephone: 763-355-2030 Web Site: www.aecnonoise.com file:Cover Eng Noise Mitigation Examples. doc y i LL x t ti 4 e V t 4 3 AEROACOUSTICS ENGINE EPIN „ ON `t!"_ A 8014 Olson Highway / #210 Minneapolis, Minnesota 55427-4712; Unitec States of Americ Time Zone: -0600 UTC/GMT; Central (USA; Web Site: www.aecnonoise.com 2815 37C?AcQusttG M4del.doC J II4 rY Jnr M y ii] R s R j 1 s i 21, 1 Vii, ij yy 11 r, .•_ t ti r' r'•}_ '{ fi waw 1 1yll 10 1, R qp t i r.' ss. 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C • tt jr' i a ' bra , 114., 1 ^ '+ t+ t,.'? ) i' • l 1 4 •. y ) t r 1 /. fir r y';,` .. 1 :. f LL r 1 1 ti From: Larry Hansen <larry.hansen@aecnonoise.com> Sent: Thursday, December 3, 2015 2:40 PM To: Stacey Hannover Cc: Pat Mason Subject:Dakota Aggregate 4 - Hour Community Noise Analysis H Dakota Aggregate P.O.# 551-1656 H AEC Job #JE01-9406 Attachments: DAL TP1 - 2200 to 2400.pdf; DAL TP1 - 2400 to 0200.pdf; DAL TP1 - 0200 to 0217.pdf, DAL TP1 - Climatic Data.pdf; DAL TP2 - 2200 to 2400.pdf, DAL TP2 - 2400 to 0200.pdf; DAL TP2 - 0200 to 0230.pdf; DAL TP2 - Climatic Data.pdf;Test Point Locations.pdf; Data- Logging Parameters.pdf,TP1 03 Nov 2015.pdf,TP2 02 Nov 2015.pdf, AEC-69900A-69903A.pdf Gentlemen: On Monday 02 and Tuesday 03 November 2015, Aeroacoustic Engineering Consultants LLC (AEC) engineers commenced a "nighttime" 4-hour (plus) acoustic test on two (2) separate sites bordering Dakota Aggregates LLC (DAL) North and West property lines. The test sequence was successfully concluded at 0217-hours Wednesday 04 December 2015 with acoustic test data and climatic conditions within protocol norms. The acoustic monitoring locations were at nominal right angles from the intersection of Biscayne Avenue and CR-42 (150th Street West) in Rosemount, MN. One site, Test Point-1 (TP-1) was located just South of the intersection on Biscayne Avenue with the monitoring station (reference attached "TP1 03 Nov 2015") installed on DAL property near the Biscayne East curb (GPS locations furnished on Test Point Locations" attachment). A second site, Test Point-2 (TP-2) was located a few hundred yards East of the intersection on CR-42 (reference attached "TP2 03 Nov 2015') on DAL property near the CR-42 South curb (GPS locations furnished on"Test Point Locations"attachment). All test locations were off road, on DAL property near respective property lines, with high visibility traffic cones and amber strobing warning beacon deployed. Each location was continuously staffed with an acoustic engineer to note any unusual aberration in protocol, activity and/or weather during test duration. The express purpose of acoustical testing was to monitor the defacto community ambient sound pressure levels emanating from the DAL and neighboring quarry activity, develop a data base for future optional) predictive computer simulations, establish a baseline test for future comparisons, identify aero/electro-mechanical generated pure tones and develop an acoustic criteria for design of future noise mitigating systems, as required. Acoustic testing was continuous throughout each 4-hour test duration and extended beyond to obtain ambient levels when all local quarry equipment was off. Vehicular activity on CR-42 for 02 November 2015 was considerably heavier than was experienced on 03 November 2015. Numerous acoustic events (local acoustic excursions above 50-dBA) were observed to be the result of vehicular traffic noise on CR-42 with a much lesser amount on Biscayne Avenue. All data is reported in nighttime hours as defined by MNPCR Chapter 7030, paragraph 7030.0020) but divided by individual test segments of 2200-hours to 2400-hours, 2400-hours to 0200-hours and additional shorter periods after 0200-hours to establish a quiescent ambient, as noted in support documentation. The data acquisition system was calibrated immediately before and after the test duration with no measurable drift indicated. Climatic conditions for each test period was seasonably warm, clear and some late fog with no prohibitive local 1 weather (reference "DAL TP1-Climatic Data" & "DAL TP2-Climatic Data," attachment). These time groupings were initially selected to accommodate staggered quarry stop times of 2400-hours for DAL and 0200-hours for neighboring Aggregate Industries. All DAL stop times were verbally confirmed with night supervisor; Aggregate Industries stop times were not confirmed. SUMMARY The data is provided in two-sets of two-hour test segments grouped in individual nighttime, time- intensity integrated subdivisions. AEC post processing will permit isolating any one or grouping a plurality of one-hour segments for customized analysis, as required. However, values of short term segments will typically vary by only a few-dB (+/- x.y-dB) from the longer duration sample, depending on acoustic events contained in selected segment(s). The LAeq (see "Data Format Discussion," following for term definitions) for the existing site acoustic ambient for each nighttime test period: TP-1; 03 November 2015 2200-hours to 2400-hours: LAeq(2)=55.5-dBA, L50 =49.2-dBA, L10 =58.8-dBA; 2400-hours to 0200- hours: LAeq(2) = 50.6-dBA, L50 = 39.7-dBA, L10 = 53.1-dBA; 0200-hours to 0217-hours: LAeq(o.25) _ 48.9-dBA, L50 = 41.0-dBA, L10 = 51.0-dBA. TP-2. 02 November 2015 2200-hours to 2400-hours: LAeq(2) = 60.7-dBA, L50 = 54.2-dBA, L10 = 64.1-dBA; 2400-hours to 0200-hours: LAeq(2) = 56.3-dBA, L50 = 44.8-dBA, L10 = 58.0-dBA; 0200-hours to 0230-hours: LAeq(0.5) = 56.7-dBA, L50 = 41.2-dBA, L10 = 58.6-dBA. OBSERVATIONS 01. Minnesota MNPCR Chapter 7030, Paragraph 7030.0040 states Noise Area Classification NAC-1 residential) nighttime land use to be a maximum: L50 of 50-dBA and L10 of 55-dBA. 2. With existing DAL quarry activity, traffic flow on CR-42 provides effective acoustic masking during peak hours of heavy usage. During lighter traffic patterns, quarry activity is acoustically perceivable. 3. During quarry activity, some aero/electro-mechanical suspected pure tones were evidenced at or near the 125-Hz third-octave (1/3-octave) frequency band within the acoustic spectrum present at property lines. DATA FORMAT DISCUSSION Each of two (2) measured, contiguous 2-hour, acoustic segments at each designated test location "TP- 1 & TP-2" (is depicted on AEC "Page 1" and graphically presented and expanded in two (2) discrete segments for"2200-hours to 2400-hours and 2400-hours to 0200-hours nighttime" time periods, plus a third segment for varied length ambient test period. In nighttime graphics, "Page 1," the vertical green lines located in the horizontal box along the top, identify acoustic events and will correlate with the events tabulated in the Acoustic Events Tables starting on "Page 2," inclusive. The vertical purple lines located in the horizontal box along the top, identify sound events and will correlate with the events tabulated in the Acoustic Events Tables starting on "Page 2" (number of pages vary with quantity of acoustic events) for nighttime, inclusive. An acoustic event may be defined as an instantaneous or impact noise of short duration but a sound event is a sustained noise that has been recorded in a computer"wav" file for reference and record. In each "Page 1" graphic, the blue plot line descriptor, "LAeq" is the equivalent continuous level for the duration of the measurement as defined by IEC 804. The green plot line descriptor, "LAFinax" is the maximum, A-weighted, Fast-Scale level within the sample measurement. The red plot descriptor 2 LLpeak)" is the maximum A-weighted peak value detected during the measurement period. The black plot descriptor, LAFMin" is the minimum, A-weighted, Fast-Scale level within the sample measurement. The full graph length, vertical red line is the cursor and digitizes any point selected and displays the values at the bottom of the graph. Periods of high and low acoustical activity are readily apparent in each presentation. A sharp rise or thin line excursion is indicative of an impact type, acoustical event. The graphic on second-to-last page for nighttime, is an acoustic spectral summary for each test measurement period. The blue descriptor "LLeq" is the continuous equivalent sound level, defined as the single sound pressure level that, if constant over the stated measurement period, would contain the same sound energy as the actual monitored sound that is fluctuating in level over the measurement period. A 2-hour LLeq is formally presented as Leq(z). If measurable, the green and red vertical bar segments represents the maximum and minimum acoustic level components, respectively, of the total Leq(period). The red, full height, vertical cursor indicates the A-weighted, Fast Response Scale, equivalent ambient sound pressure level and digitized associate descriptors, over each designated test period. The graphic on the last page for nighttime is a graphical presentation of the cumulative distribution of the "LAeq" acoustic levels measured with cardinal fractile values tabulated in the upper right hand corner. The "LAeq" descriptor represents acoustic levels measured on the A-weighted, Fast- Scale. The red line graph indicates the statistical distribution of the daytime, nighttime and/or 2-hour test acoustic levels. The red vertical cursor identifies the selected sound pressure level and digitizes the pertinent data as a percent of the total measurement time. The tabulated fractile values (Ln) are percentile levels, where "n" can be any number between 0 and 100 (noninclusive). The number designated by "n" corresponds to the percentage of measurement time period by which the stated sound level has been exceeded. For example, in a hypothetical case, the descriptor "15 = 68.4 dBL" means that the acoustical levels exceeded 68.4 dBL over 5% of the time designated measurement period (for this example of a duration of 24-hours, 72 total minutes out of 1,440 contiguous minutes of testing). All two (2) second, or more, sustained acoustical events exceeding preset criteria, for the duration of each 2-hour test segment, are tabulated in the Events Table starting on "Pages 2"for nighttime. Picture of the test area and associated test set-up may be found in the "DSCN3676" photograph attachment. A sketch of the test site may be found in the "Test Point Locations" drawing attachment. Definition of various acoustic descriptors may be found in the "Data-Logging Parameters" attachment. Meteorological data for the specific test site location is included in the "Site Climatic Data 1-2 Dec 2014" attachment. Local weather samples were data logged every five-minutes (5-minutes)for the entire test duration. Wind speed and direction were measured at an elevation of eight (8) feet above grade to ascertain impact on the acoustic microphone. Barometric pressure measurements have not been normalized for altitude or local elevation. All references to compass direction is magnetic with no declination corrections. BACKGROUND To assist in determining empirical acoustical emissions around the DAL quarry perimeter, two (2) separate 4-hour sound monitoring tests were accomplished. At each location, approximate curb-side measuring position were selected at point nearest in proximity to two (2) intersecting DAL property lines. Acoustic data was automatically logged for acontiguous 4-hour duration (plus time after quarry shutdown) at the rate of one (1) complete spectrum every 60-seconds for each test segment duration. 3 When an acoustic event occurred that exceeded a preset criteria, the data acquisition system was programed to log at an increased rate of one (1) each acoustic spectra per one (1) second (including time and date) until the noise level retreated below criteria trigger level. Subsequently, for the duration of a triggered acoustical event, the data acquisition system activated a precision, computer digitizer to simultaneously log a high fidelity "wav" sound recording and time/date-file correlation for future reference. On the graphic plot"PAGE 1,"the green vertical lines (located in the horizontal bar near the top) identify individual and grouped acoustic events. In the body of the graph, the function of color plots may be selected from a score of acoustic descriptors which will conform to the pertinent noise regulation. The attached events table, starting on Page 2, delineates a digital summary of all acoustic events occurring during the nighttime 4-hour measurement period (LAeq, LAFinax & LAFmin) including Marked," "Unmarked" and "Total' as well as "Duration." The "Time-Date" event entry correlates the tabulated data directly to the graphic plot and "wav" recording of the actual sound that triggered the event. As previously noted, acoustic descriptors for the table may be selected from scores of units but are usually dictated by the language of the local environmental zoning law or regulation. At any point in time, an acoustic "slice" may be called to display an entire spectrum for an "event" or regular sampling. There is a plethora of logged data available for post processing studies. It should be noted that the time of day cited in all graphics and tabular data was automatically logged, within the electronic data gathering system, by an internal clock set to the Central Standard time zone UTC -6.0) of the United States of America. No correction factor need be applied for Rosemount, MN local time. The acoustic data base herein presented may be utilized in a computer model of the acoustic environment of a precise, geographical area around the subject site for prediction and control of environmental noise. The AEC proprietary computer simulation program, Computer Acoustic Simulation & Analysis (CASA), provides a 3-dimensional computer model to predict and assess the acoustic impact from physical changes on area noise propagation, before the fact. A descriptive specification (bulletin number AEC-69900A) on CASA has been included as an attachment to this report. Thank you for the opportunity to be of service. Please feel free to contact us with any questions or concerns. Regards, Larry Hansen Aeroacoustic Engineering Consultants, LLC 8014 Olson Memorial Highway/#210 Minneapolis, MN 55427-4712 United States of America Direct Dial: 763-546-8565 Mobile: 612-220-7026 Main Office: 763-355-2030 Time Zone: -0600 UTC/GMT; Central Standard (USA) E-mail:larry.hansen(a)aecnonoise.com Web Site:www.aecnonoise.com 4 ggregates1 TestR •int LocationsIT P2 ( 44" 44'20 70"N 93 62140"W TP1 ( 44 43'56 20",N, 93" 6'57.10"W) rb cr ji E. 7- GOO ile-earth N 2015iie 3000 ft t t l i ii ;. a, w.. i 4 i , F , 7 4 i i Y V t Master Parameters: AEC Project#J01-9406 Date: 02 December 2015 Prepared For: Dakota Aggregates LLC, Cntr. Pt. Blvd./Ste. 300, Mendota Heights, MN 55120 Page: 1 of 3 MAJOR ACOUSTIC DATA-LOGGING PARAMETERS 1.1 What is Measured and Recorded 1.1.1 Introduction In this specification, instantaneous values for parameters marked: are replaced by a new one every second. are replaced by a new one every three seconds. are replaced by a new one every five seconds. All others are currently valid for the time elapsed since the measurement start. 1.1.2 Discrete Parameters During a Measurement The following is a list of broad-band discrete parameters measured by the analyzer. The X and Y refer respectively to frequency weightings A, C or L) and time weightings (S, F or 1). Elapsed time: Time elapsed since start of measurement. x Peaks: Number of peak levels(separated by 1 s or more)exceed a user-defined value during a measurement. Lxpk (MaxP.): Maximum Peak value detected during the measurement. Lxpk (Peak)*: ($) Peak value. LxY (SPL)*: (#) Maximum value of RMS level in 1-second interval as defined by IEC 651. Continued . . . . .) Replaced 15 times per second when displayed graphically Master Parameters:AEC Project#J01-9406 Date: 02 December 2015 Prepared For: Dakota Aggregates LLC, Cntr. Pt. Blvd./Ste. 300, Mendota Heights, MN 5512 Page: 2 of 3 LxY (Inst.)*: ($) Last sampled instantaneous value of RMS level as defined by IEC 651 and JIS C1505. LXYT3: (#) 3-second Taktmaximal value as defined by TA Larm and VDI 2058. LXYT5: (#) 5-second Taktmaximal value as defined by TA Larm and VDI 2058. LAE(AS EL): A-weighted sound exposure level for the duration of the measurement as defined by IEC 804. Lxeq: Equivalent continuous level for the duration of the measurement as defined by IEC 804. LXIm: Equivalent continuous impulse for the duration of the measurement as defined by IEC 804, Appendix B. LXeq- LAeq: Can be used as a measure of low-frequency spectral content if X = C. LAIm-Laeq: Can be used as a measure of impulsive content. LXYTm3: Average 3-second Taktmaximal value for the duration of the measurement as defined by TA Larm and VDI 2058. LXYTm5: Average 5-second Taktmaximal value for the duration of the measurement as defined by TA Larm and VDI 2058. Continued . . . . .) Replaced 15 times per second when displayed graphically Master Parameters:AEC Project#JO1-9406 Date: 02 December 2015 Prepared For: Dakota Aggregates LLC, Cntr. Pt. Blvd./Ste. 300, Mendota Heights, MN 5512 Page: 3 of 3 LXY Max: Maximum LXY value detected within the elapsed time. LXYN 1 User-defined percentilelevel where the value of LXYN1 isdenedpece exceeded for N1% of the elapsed time (N = 0 to 100%). LXYN2: User-defined percentile level where the value of LXYN2 is exceeded for N2% of the elapsed time (N = 0 to 100%). LXYN3: User-defined percentile level where the value of LXYN3 is exceeded for N3% of the elapsed time (N = 0 to 100%). LXYN4: User defined percentile level where the value of LXYN4 is exceeded for N4% of the elapsed time (N = 0 to 100%). LXYN5: User-defined percentile level where the value of LXYN5 is exceeded for N5% of the elapsed time (N = 0 to 100%). LXY Min: Minimum LXY value detected within the elapsed time. LAEP,d: Daily A-weighted Personal Noise Exposure Level as defined by EEC 88/186. This is the 8 hour noise dose of a constant A-weighted sound level which lasts for a period of time Te but is measured only over a time T. Above are just a few of the most frequently specified acoustic descriptors used in national and international regulations. There are scores of additional descriptors not listed but available to comply with all international standards or for customized analysis. END OF SPECIFICATION - AEROACOUSTIC ENGINEERING CONSULTANTS, LLC 8014 Olson Highway, #210 Minneapolis, MN 55427-4712 Telephone: (763) 355-2030; Web Site: www.aecnonoise.com File:Data-Logging Parameters.wpd ENVIRONMENTAL NOME & 1*9-1.D wig oo M IMPAIRMENT LIABILITY ANALYSIS s + Iii a ..;' a R ` .. i ittK..(,r• f ' •, pro F DOW ilk9 1 1 1 is w•i PREDICTIVE COMPUTER yr ;. spy f SIMULATIONS ANALYSIS Y SERVICE" AER®ACOUSTIC ENGINEERING CONSULTANTS, LLC BO 4 OLSON MEMORIAL HIGHWAY / s#210 MINNEAPOLIS, MN 55437-471 2 UNITED STATES OF AMERICA PHONE: 763-355-2030, FAX: 763-544-1149 AEC-69900A COMPUTER ACOUSTIC SIMULATION & ANALYSIS (CASA) O Creating noise maps based on prediction using real data and/or projected O Identifying of prominent noise sources O Proposing and showing the effect of noise reduction solutions prior to implementation O Ranking noise sources by SPL Monitoring and controlling the noise environment of a geographical area O Industry can ensure compliance with environmental legislation Figure 1 O Identify and provide solutions to noise problemsAcousticData&Precise GPS Location Acquisition Basic Concept: CASA is used to make an electronic model of the acoustic environment of a geographical area, for the prediction and control of outdoor noise. CASA software improves upon traditional calculation techniques, by allowing easy change and re-calculation of the mathematical model, giving the client the chance to compare a number of different scenarios. Noise level prediction is a widely used tool for predicting the noise impact of changes in the noise environment, such as land development, changes to machinery or building use. This technique is also used to plan or design environments, where noise management is necessary. In complex environments, it can be difficult with traditional techniques to see exactly how much each noise source contributes to the overall noise picture. CASA can do this by ranking the individual noise sources to clearly show the importance of each source. The effect of noise Figure 2 reduction can also be studied by introducing a reduction to the emissionAcousticTestData For Calibration of CASA Model groupsofasource (or g p s of sources)' CASA makes available immediate what if' results, for example, "what if all exhaust ventilators are reduced by 6 dB?" Moreover, color-coded sound pressure contours (see front) visualize the situation in an easy to understand way. Quite often with traditional measurements, it is not possible to accurately measure the noise emission from a single factory or road due to the existence of other noise sources which cannot be shut off, for example a neighboring Y factory. In such cases, sound power levels can be measured and the results assigned to a factory group created in the CASA model. CASA then takes account of the contribution from the various noise sources, and is able to "switch off' specific sources allowing easy identification ti and isolation of a noise source, and indications of potential noise problems. The result of calculations can be shown as a suite of result tables (see Figure 3 Figure 3) and/or as graphical presentations (see front). CASA can Typical Results Tables Generated By CASA quickly verify that the model represents reality and identify noise problems, by comparing predicted values to legal limits. AEROACOUSTIC ENGINEERING CONSULTANTS, LLC 01 4 OLSON MEMORIAL HIGHWAY / #21 0 MINNEAPOLIS, MN 55427-471 2 PHONE: 763-355-2030, FAx: 763-544-1149 WEBSITE: WWW.AEONONOISE.COM AEC-69903A Let a qualified AEC engineer assist you to establish an effective protocol and implementation schedule. Let our 30 years of experience with NOISE make your job easier. 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ul ul ul V1 Vl to ul Vl In o ul Vl In ul ul Vl ul In In ul o ul ul Vl ul aEF Vl M N IA W. l0 Vl N N Ol n vi CI M M a d' M a a M N N N N N tD tD Ol c0 w a M N N N Ill Ol Ol Ol ul Vl In Ill ul o0 o0 ul M N N N Ol n tD Vl tD ul ul ul O Vl a a M Ln m o oo n n N r n to to to to to to o o 6 D D to o L6 to to 6 ' n ` n vi ui Iri vi vi Ln v ui A a v v A m In n ^ a v v tr v c v m m m m m m m m m m m m m aEH O Q Q Q Q Q Q Q Q Q Q Q Q Q Q Q Q Q Q Q Q a a a Q Q Q a o ul o ul O IA o ul 0 o O o O ul o o o ul O N o ul o o o LA o VI 0 o o N o Vl O mo Vl O mo o O ul o Vl O o o N O ul o Vl O In O ul o Ill O o O ul o w N M M a C Vl vl O O rl '- I N N M M 19: a Vl In 9 0 .,- i N N N to M a VT Ill ul O O N M M V a Vl Vl O O N 7i N N ni M a a Vf Vl O O rl r- I N E Ol Ol Ol Ol Ol Ol Ol Ol Ol Ol Ol Ol O O O O O O O O O O O O e- I .-- I .-- I '- I e- I e- I - e- 1 N N N N N N N N N N N N N N N N e- I - 1 a- i r- I N '- I r- 1 H N N N N N N N N N In In VI o In Ln ul In Ill ul Ill Ill Ill Ln Ill o N o Vl Vl Ill IA Vl In ul ul ul ul o ul to Vl Ill o o Ill Ill o ul Ill Vl o o ul o Vl o o o Vl ul Vl o o Ill ul Vl ul Vl ul o ul ul Vl ul O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N M M M M M M M M M M M M M M M M M M M M M M M M M M M M M M M M M M M M a a 0 a tf a V a V a V a a a7 t7 a s tf a a a tf a tt a a- a t7 tt I -- I -- I -- I -- 1 -- 1 -- I -- I -- I -- I -- I -- I -- 1 -- 1 -- I -- I -- I -- I -- 1 -- 1 -- 1 - -- I -- I r\- 1 c\- I -- I -- 1 -- 1 -- I -- I N - e\- I - -- I N - -- I -- I -- I - -- I -- I -- I -- 1 N N -- I -- 1 -- I -- I -- I -- I N -- 1 -- I -- I -- I -- I -- I -- I -- 1 -- 1 r- 1 .-- I r- 1 r- 1 - .- 4 r- 1 - N N N N N N N N -- I e- I N N N .-- 1 N N N e- I e- 1 N r- 1 r- I a- I N N e- I r- 1 r- I r- I e- I .-- I - r- 1 r- I e- I WmD s Dakota Aggregates TP2 10pm to 12am in Calculations M Event Sound dB 100 I I I I I I I i I 90 I I I I 70 fyrq, u 60 50 I I I I I f I I I I I I I I I I 40--- 30--- 10:00:00 0 10:00:00 PM 10:20:00 PM 10:40:00 PM 11:00:00 PM 11:20:00 PM 11:40:00 PM 12:00:00 AM LAeq LAFinax LLpeak LAFmin Cursor: 11/02/2015 10:47:50 PM - 10:47:51 PM LAeq=78.5 dB LAFinax=79.5 dB LLpeak=100.0 dB LAFmin=77.1 dB 1 Dakota Aggregates TP2 10pm to 12am in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time dBj fdBld6 Total 11/02/2015 10:00:00 PM 2:00:11 0.0 60.7 79.5 37.9 Unmarked 11/02/2015 10: 14:40 PM 0:38:09 0.0 49.4 61.0 37.9 All) Event 11/02/2015 10:00:00 PM 1:22:02 0.0 62.2 79.5 44.4 All Sound 11/02/2015 10: 15:22 PM 0:21:37 0.0 62.3 78.3 44.4 Event 11/02/2015 10:00:00 PM 0:14:40 0. 0 62.8 77.3 48.3 Event 11/02/2015 10:15:22 PM 0:01:04 0.0 60.8 72.9 48.7 Event 11/02/2015 10:17:03 PM 0:02:19 0.0 63.2 77.8 48.7 Event 11/02/2015 10: 19:43 PM 0:07:11 0.01 64.3 76.3 47.7 Event 11/02/2015 10:27:41 PM 0:00:17 0.0 56.8 64.1 47.2 Event 11/02/2015 10:28:05 PM 0:01:52 0.0 61.4 74.6 47.7 Event 11/02/2015 10:30:17 PM 0:00:29 0.0 58.0 65.6 46.7 Event 11/02/2015 10:31:47 PM 0:06:27 0.0 63.1 77.0 47.6 Event 1 11/02/2015 10:38:44 PM 0:02:42 0.0 64.8 76.4 49.0 Event 11/02/2015 10:42:08 PM 0:06:59 0.0 61.51 79.5 48.5 Event 11/02/2015 10:50:00 PM 0:00:54 0.0 55.8 67.0 48.2 Event 11/02/2015 10:51:53 PM 0:00:35 0.0 59.2 68.7 47.8 Event 11/02/2015 10:53:48 PM 0:00:17 0.0 58.0 65.3 46.9 Event 11/02/2015 10:54:38 PM 0:01:37 0.0 64.9 77.3 48.6 Event 11/02/2015 10:56:53 PM 0:00:17 0.0 57.9 67.2 48.2 Event 11/02/2015 10:58:06 PM 0:00:13 0.01 58.6 66.2 47.7 Event 11/02/2015 10:59:30 PM 0:00:23 0.0 59.0 67.7 47.5 Event 11/02/2015 11:00:15 PM 0:01:14 0.0 60.9 70.9 48.8 Event 11/02/2015 11:02:20 PM 06-03:01 0.0 61.3 73.3 48.8 Event 11/02/2015 11:05:46 PM 0:00:55 0.0 60.2 68.3 47.7 Event 11/02/2015 11:07:43 PM 0:00:37 0.0 58.3 67.1 48.2 Event 11/02/2015 11:09:00 PM 0:01:15 0.0 60.9 74.2 48.5 Event 11/02/2015 11:10:44 PM 0:00:49 0. 0 63.1 71.6 47.8 Event 11/02/2015 11:12:09 PM 0:00:29 0.0 54.8 64.3 46.6 Event 1 11/02/2015 11:13:09 PM 0:01:55 0.0 59.8 71.9 47.9 Event 11/02/2015 11:16:50 PM 0:00:52 0.0 60.3 72.3 48.2 Event 11/02/2015 11:18:01 PM 0:00:55 0.0 61.9 70.6 48.6 Event 11/02/2015 11:19:32 PM 0:01:351 0.0 61.0 72.0 48.7 Event 11/02/2015 11:21:30 PM 0:04:35 0.0 61.3 74.2 48.7 2 Dakota Aggregates TP2 10pm to 12am in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time dB d6 dB Event 11/02/2015 11:26:29 PM 0:00:44 0.0 61.5 71.9 48.3 Event 11/02/2015 11:27:44 PM 0:02:56 0.0 62.8 77.3 48.3 Event 11/02/2015 11:31:33 PM 0:00:24 0.0 60.6 71.1 48.6 Event 11/02/2015 11:32:39 PM 0:00:16 0.0 57.7 66.2 48.1 Event 11/02/2015 11:33:36 PM 0:00:26 0.0 60.6 69.5 47.5 Event 11/02/2015 11:36:30 PM 0:00:24 0.0 58.2 65.2 46.6 Event 11/02/2015 11:38:22 PM 0:00:46 0.0 64.8 78.3 48.9 Event 11/02/2015 11:39:32 PM 0:01:13 0.0 59.1 70.7 46.3 Event 11/02/2015 11:41:04 PM 0:00:43 0.0 62.0 73.8 47.9 Event 11/02/2015 11:43:13 PM 0:00:53 0.0 59.9 71.3 46.7 Event 11/02/2015 11:45:11 PM 0:00:13 0.0 60.1 67.7 44.4 Event 11/02/2015 11:45:46 PM 0:00:10 0.0 57.7 64.6 47.8 Event 11/02/2015 11:46:05 PM 0:00:18 0.0 58.4 66.3 46.4 Event 11/02/2015 11:46:53 PM 0:00:14 0.01 59.0 66.4 45.8 Event 11/02/2015 11:47:20 PM 0:00:18 0.0 56.3 63.0 46.0 Event 11/02/2015 11:48:30 PM 0:01:16 0.0 61.1 72.1 47.8 Event 11/02/2015 11:51:03 PM 0:00:22 0.0 58.9 68.8 47.1 Event 11/02/2015 11:52:30 PM 0:01:52 0.0 60.1 74.7 46.9 Event 11/02/2015 11:54:45 PM 0:00:25 0.0 59.3 69.0 48.0 Event 11/02/2015 11:55:32 PM 0:00:25 0.0 63.5 72.8 47.4 Event 11/02/2015 11:57:04 PM 0:00:59 0.0 59.3 70.6 47.2 Event 11/02/2015 11:58:52 PM 0:00:17 0.0 61.3 69.9 45.2 Sound 11/02/2015 10:15:22 PM 0:00:30 0.0 60.0 67.6 51.0 Sound 11/02/2015 10: 17:03 PM 0:00:30 0.0 67.9 77.8 51.9 Sound 11/02/2015 10:19:43 PM 0:00:30 0. 0 68.4 76.0 53.5 Sound 11/02/201510:27:41 PM 0:00:17 0. 0 56.8 64.1 47.2 Sound 11/02/2015 10:28:05 PM 0:00:30 0.0 58.6 67.2 50.5 Sound 11/02/2015 10:30:17 PM 0:00:29 0.0 58.0 65.6 46.7 Sound 11/02/2015 10:31:47 PM 0:00:30 0.0 57.4 67.2 49.7 Sound 11/02/2015 10:38:44 PM 0:00:30 0.0 66.41 74.9 53.4 Sound 11/02/2015 10:42:08 PM 0:00:30 0.0 59.1 68.8 50.8 Sound 11/02/2015 10:50:00 PM 0:00:30 0.0 57.7 67.0 51.4 Sound 11/02/2015 10:51:53 PM 0:00:30 0.0 59.8 68.7 49.4 Sound 11/02/2015 10:53:48 PM 0:00:17 0.0 58.0 65.3 46.9 Sound 11/02/2015 10:54:38 PM 1 0:00:30 0.01 66.2 1 77.3 52.8 3 I Dakota Aggregates TP2 10pm to 12am in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time- 1% 1 fdBId6 d6 Sound 11/02/2015 10:56:53 PM 0:00:17 0.0 57.9 67.2 48.2 Sound 11/02/2015 10:58:06 PM 0:00:13 0.0 58.6 66.2 47.7 Sound 11/02/2015 10:59:30 PM 0:00:23 0.0 59.0 67.7 47.5 Sound 11/02/2015 11:00:15 PM 0:00:30 0.0 61.0 70.9 50.4 Sound 11/02/2015 11:02:20 PM 0:00:30 0.0 60.1 66.4 52.7 Sound 11/02/2015 11:05:46 PM 0:00:30 0.0 59.4 67.6 51. 5 Sound 11/02/2015 11:07:43 PM 0:00:30 0.0 59.1 67.1 49.9 Sound 11/02/2015 11:09:00 PM 0:00:30 0.0 56.31 65.3 48.9 Sound 11/02/2015 11:10:44 PM 0:00:30 0.0 64.9 71.6 54.1 Sound 11/02/2015 11:12:09 PM 0:00:29 0.0 54.8 64.3 46.6 Sound 11/02/2015 11:13:09 PM 0:00:30 0.0 62.3 71.9 53.1 Sound 11/02/2015 11:16:50 PM 0:00:30 0.0 62.3 72.3 51. 5 Sound 11/02/2015 11:18:01 PM 0:00:30 0.0 62.3 1 70.6 53.4 Sound 11/02/2015 11:19:32 PM 0:00:30 0.0 64.1 72.0 52.6 Sound 11/02/2015 11:21:30 PM 0:00:30 0.0 59.5 69.1 52.0 Sound 11/02/2015 11:26:29 PM 0:00:30 0.0 63.0 71.9 52.5 Sound 11/02/2015 11:27:44 PM 0:00:30 0. 0 66.2 74.8 52.4 Sound 11/02/2015 11:31:33 PM 0:00:24 0.0 60.6 71.1 48.6 Sound 11/02/2015 11:32:39 PM 0:00:16 0.0 57.7 66.2 48.1 Sound 11/02/2015 11:33:36 PM 0:00:26 0.0 60.6 69.5 47.5 Sound 11/02/2015 11:36:30 PM 0:00:24 0.0 58.2 65.2 46.6 Sound 11/02/2015 11:38:22 PM 0:00:30 0.0 66.6 78.3 50.7 Sound 11/02/2015 11:39:32 PM 0:00:30 0.0 56.4 63.4 50.5 Sound 11/02/2015 11:41:04 PM 0:00:30 0.0 63.4 73.8 52.0 Sound 1 11/02/2015 11:43:13 PM 0:00:30 0.0 61.8 71.3 48.9 Sound 11/02/2015 11:45:11 PM 0:00:13 0.0 60.1 67.7 44.4 Sound 11/02/2015 11:45:46 PM 0:00:10 0. 0 57.7 64.6 47.8 Sound 11/02/2015 11:46:05 PM 0:00:18 0.0 58.4 66.3 46.4 Sound 11/02/2015 11:46:53 PM 0:00:14 0.0 59.01 66.4 45.8 Sound 11/02/2015 11:47:20 PM 0:00:18 0.0 56.3 63.0 46.0 Sound 11/02/2015 11:48:30 PM 0:00:30 0.0 62.5 72.1 49.7 Sound 11/02/2015 11:51:03 PM 0:00:22 0.0 58.9 68.8 47.1 Sound 11/02/2015 11:52:30 PM 0:00:30 0.0 63.8 74.7 53.7 Sound 11/02/2015 11:54:45 PM 0:00:25 0.0 59.3 69.0 48.0 Sound 11/02/2015 11:55:32 PM 0:00:25 0.0 63.5 72.8 47.4 4 0 Dakota Aggregates TP2 10pm to 12am in Calculations Name Start Elapsed Overload LAeq LAFinax N45.. i time time dB dB Sound 11/02/2015 11:57:04 PM 0:00:30 0.0 61.0 70.6 Sound 11/02/2015 11:58:52 PM 0:00:17 0.0 61.3 69.9 5 Dakota Aggregates TP2 10pm to 12am in Calculations dB 11/02/2015 10:00:00 PM - 12:00:11 AM Total 100- 90- 80 - 70- 6 0 0090 80 70 60 50 40 30 20 - 10 6.30 16 31.50 63 125 250 500 1000 2000 4000 8000 16000 A L Hz LLeq Cursor: (A) Leq=60.7 dB 6 Dakota Aggregates TP2 10pm to 12am in Calculations Based on LAeq, 1s Class width: 1.0 dB 11/02/2015 10:00:00 PM - 12:00:11 AM Total 100 L1 = 72.2 dB L5 = 66.9 dB 90 i - - -i- - - - - - - L10 = 64.1 dB L50 = 54.2 dB 80- L90 = 46.6 dB L95 = 43.9 dB L99 = 40.3 dB 70 r - rt - - - -i - -- - - - - - r - - - -i - - 60 - 50 i - - - - - - - -- - i- - - 40 30 20 10- 0 0 1 20 30 40 50 60 70 80 90 100 dB Level Cumulative Cursor: [50.0 ; 51.0[ dB Level: 6.3% Cumulative: 75.1% Dakota Aggregates TP2 12am to 2am in Calculations E Event Sound dB 100 I I I I i I I 1 I I f I I I I I I I I i 90 I - - - - - - i- - 80- 70 0 70 i1 1 a i 60- 50 0- 50 i 40 I I I I I I I I I I I 12:00:00 AM 12:20:00 AM 12:40:00 AM 01:00:00 AM 01:20:00 AM 01:40:00 AM 02:00:00 AM LAeq LAFinax LLpeak LAFmin Cursor: 11/03/2015 12:58:31 AM - 12:58:32 AM LAeq=81.1 dB LAFinax=82.2 dB LLpeak=96.6 dB LAFmin=79.2 dB 1 Dakota Aggregates TP2 12am to 2am in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time dBj [dBI fdBI Total 11/03/2015 12:00:00 AM 2:00:09 0.0 56.3 82.2 28.7 Unmarked 11/03/2015 12:00:00 AM 1:26:51 0.0 45.2 59.3 28.7 All Event 11/03/2015 12:00:32 AM 0:33:18 0.0 61.61 82.2 43.6 All Sound 1 11/03/2015 12:00:32 AM 0:24:23 0.0 62.1 80.1 43.6 Event 11/03/2015 12:00:32 AM 0:00:44 0.0 62.2 74.4 47.7 Event 11/03/2015 12:01:52 AM 0:00:17 0.0 59.0 67.5 46.0 Event 11/03/2015 12:02:51 AM 0:00:24 0.0 60.1 69.6 47.2 Event 11/03/2015 12:03:32 AM 0:00:41 0.0 63.01 73.8 47.6 Event 1 11/03/2015 12:06:55 AM 0:00:33 0.0 57.6 68.1 47.3 Event 11/03/2015 12:07:31 AM 0:00:19 0.0 60.9 70.3 47.6 Event 11/03/2015 12:09:20 AM 0:00:24 0.0 62.3 69.1 46.6 Event 11/03/2015 12: 10:52 AM 0:00:57 0.0 60.5 74.2 47.8 Event 11/03/2015 12:12:04 AM 0:01:18 0.0 61.2 72.5 44.8 Event 11/03/2015 12:14:08 AM 0:00:23 0.0 60.9 72.1 47.7 Event 1 11/03/2015 12: 14:39 AM 0:00:50 0.0 62.91 70.4 48.6 Event 11/03/2015 12:16: 12 AM 0:00:16 0.0 60.6 67.7 47.2 Event 11/03/2015 12:16:40 AM 0:00:12 0.0 60.7 67.7 45.6 Event 11/03/2015 12:18:24 AM 0:00:14 0.0 59.8 67.6 45.8 Event 11/03/2015 12:19:21 AM 0:00:15 0.0 63.0 72.1 47.1 Event 11/03/2015 12:20:17 AM 0:01:52 0.0 62.4 75.0 47.0 Event 11/03/2015 12:23:08 AM 0:00:20 0.0 59.5 67.7 48.3 Event 11/03/2015 12:23:36 AM 0:00:14 0.0 59.5 67.2 45.5 Event 11/03/2015 12:24:29 AM 0:00:12 0.0 59.8 68.4 47.7 Event 11/03/2015 12:25:08 AM 0:00:51 0.0 61. 4 71.1 47.7 Event 11/03/2015 12:26:04 AM 0:00:12 0.0 57.5 64.2 47.0 Event 11/03/2015 12:27:10 AM 0:00:10 0.0 55.1 58.8 47.1 Event 11/03/2015 12:27:26 AM 0:00:14 0.0 60.9 69.4 45.7 Event 11/03/2015 12:27:47 AM 0:00:11 0.0 58.5 65.9 47.2 Event 11/03/2015 12:28:59 AM 0:01:35 0.0 60.8 73.1 47.0 Event 1 11/03/2015 12:31:05 AM 0:00:36 1 0.01 58.8 69.9 48.6 Event 11/03/2015 12:31:46 AM 0:00:58 0.0 60.81 73.7 46.8 Event 11/03/2015 12:37:59 AM 0:00:13 0.0 58.0 1 64.9 43.6 Event 11/03/2015 12:39:20 AM 0:00:10 0.0 55.01 61.4 1 46.4 2 JAZZ Dakota Aggregates TP2 12am to tam in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time d6 d6 d6 Event 11/03/2015 12:40:27 AM 0:00:20 0.0 62.0 71.4 46.4 Event 11/03/2015 12:42:16 AM 0:00:19 0.0 61.5 70.5 46.2 Event 11/03/2015 12:44:42 AM 0:00:37 0.0 60.9 72.0 48.7 Event 11/03/2015 12:45:54 AM 0:00:29 0.0 57.8 67.0 44.1 Event 1 11/03/2015 12:46:57 AM 0:00:16 0.0 61.6 71.1 46.1 Event 11/03/2015 12:51:51 AM 0:00:49 0.0 61.6 70.6 48.9 Event 11/03/2015 12:53:46 AM 0:00:25 0.0 60.0 69.2 47.7 Event 11/03/2015 12:58:01 AM 0:01:05 0. 0 66.8 82.2 46.1 Event 11/03/2015 01:04:01 AM 0:00:16 0.01 60.1 67.3 47.7 Event 11/03/2015 01:05:05 AM 0:00:31 0.0 62.8 73.9 48.7 Event 11/03/2015 01:07:13 AM 0:00:28 0.0 65.0 76.4 47.8 Event 11/03/2015 01:07:51 AM 0:00:57 0.0 61.3 69.0 46.3 Event 11/03/2015 01:10:24 AM 0:00:41 0.0 59.1 69.3 46.9 Event 11/03/2015 01:11:11 AM 0:00:25 0.0 61.4 70.7 45.3 Event 11/03/2015 01:15:00 AM 0:00:20 0.0 64.4 73.9 44.2 Event 11/03/2015 01:16:22 AM 0:00:27 0. 0 60.9 69.8 48.6 Event 11/03/2015 01:17:20 AM 0:00:26 0.0 60.1 69.3 48.3 Event 11/03/2015 01:19:09 AM 0:00:13 0.0 59.9 68.5 46.2 Event 11/03/2015 01:21:52 AM 0:00:16 0.0 59.3 66.9 46.8 Event 11/03/2015 01:22:52 AM 0:00:33 0.0 60.5 70.5 46.2 Event 11/03/2015 01:24:33 AM 0:00:24 0.0 62.1 71.9 45.7 Event 11/03/2015 01:26:36 AM 0:00:25 0.0 61.4 70.9 46.1 Event 11/03/2015 01:33:12 AM 0:00:18 0.0 58.0 65.3 46.8 Event 11/03/2015 01:33:32 AM 0:00:46 0.0 65.7 79.7 44.9 Event 11/03/2015 01:36:58 AM 0:01:27 0.0 62.1 1 74.6 47.6 Event 11/03/2015 01:39:40 AM 0:00:12 0.0 59.5 67.6 44.6 Event 11/03/2015 01:40:54 AM 0:00:08 0.0 53.9 57.6 46.6 Event 11/03/2015 01: 41:07 AM 0:00:13 0.0 59.2 65.7 45.5 Event 11/03/2015 01: 41:55 AM 0:00:11 0.0 58.8 65.9 46.8 Event 11/03/2015 01:44:36 AM 0:00:20 0.0 60.9 1 70.2 45.7 Event 11/03/2015 01:45:32 AM 0:00:11 0. 0 57.6 63.5 44.8 Event 1 11/03/2015 01:46:21 AM 0:00:54 0.0 60.0 71.7 47.9 Event 11/03/2015 01:47:25 AM 0:00:30 0.0 59.7 71.4 45.9 Event 11/03/2015 01:52:33 AM 0:00:40 0.0 59.9 69.9 46.5 Event 111/03/2015 01:55:00 AM 1 0:00:21 1 0. 0 59.8 69.7 47.1 3 Dakota Aggregates TP2 12am to 2am in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time dBj [dBj fdBI Event 11/03/2015 01:57:02 AM 0:00:23 0.0 62.0 71.2 46.2 Event 11/03/2015 01:58:44 AM 0:00:27 0.0 60.8 70.4 45.9 Sound 11/03/2015 12:00:32 AM 0:00:30 0.0 63.3 74.4 52.1 Sound 11/03/2015 12:01:52 AM 0:00:17 0.0 59.01 67.5 46.0 Sound 11/03/2015 12:02:51 AM 0:00:24 0.0 60.1 69.6 47.2 Sound 11/03/2015 12:03:32 AM 0:00:30 0.0 64.2 73.8 50.4 Sound 11/03/2015 12:06:55 AM 0:00:30 0.0 58.0 68.1 49.0 Sound 11/03/2015 12:07:31 AM 0:00:19 0.0 60.9 70.3 47.6 Sound 11/03/2015 12:09:20 AM 0:00:24 0.0 62.3 69.1 46.6 Sound 11/03/2015 12:10:52 AM 0:00:30 0.0 62.5 74.2 49.4 Sound 11/03/2015 12: 12:04 AM 0:00:30 0. 0 59.5 67.5 53.0 Sound 11/03/2015 12:14:08 AM 0:00:23 0.0 60.9 72.1 47.7 Sound 11/03/2015 12:14:39 AM 0:00:30 0.0 64.8 70.4 53.1 Sound 11/03/2015 12:16:12 AM 0:00:16 0.0 60.6 67.7 47.2 Sound 11/03/2015 12:16:40 AM 0:00:12 0.01 60.7 67.7 45.6 Sound 11/03/2015 12:18:24 AM 0:00:14 0.0 59.8 67.6 45.8 Sound 11/03/2015 12: 19:21 AM 0:00:15 0.0 63.0 72.1 47.1 Sound 11/03/2015 12:20:17 AM 0:00:30 0.0 64.9 75.0 49.9 Sound 11/03/2015 12:23:08 AM 0:00:20 0.0 59.5 67.7 48.3 Sound 11/03/2015 12:23:36 AM 0:00:14 0.0 59.5 67.2 45.5 Sound 11/03/2015 12:24:29 AM 0:00:12 0.0 59.8 68.4 47.7 Sound 11/03/2015 12:25:08 AM 0:00:30 0.0 62.1 71.1 51.3 Sound 11/03/2015 12:26:04 AM 0:00:12 0.0 57.5 64.2 47.0 Sound 11/03/2015 12:27:10 AM 0:00:10 0.0 55.1 58.8 47.1 Sound 11/03/2015 12:27:26 AM 0:00:14 0.0 60.91 69.4 45.7 Sound 11/03/2015 12:27:47 AM 0:00:11 0.0 58.5 65.9 47.2 Sound 11/03/2015 12:28:59 AM 0:00:30 0.0 63.7 73.1 47.7 Sound 11/03/2015 12:31:05 AM 0:00:30 0.0 59.5 69.9 49.6 Sound 11/03/2015 12:31:46 AM 0:00:30 0.0 63.2 73.7 49.8 Sound 11/03/2015 12:37:59 AM 0:00:13 0.0 58.0 64.9 43.6 Sound 11/03/2015 12:39:20 AM 0:00:10 0.01 55.0 61.4 46.4 Sound 11/03/2015 12:40:27 AM 0:00:20 0.0 62.0 71.4 46.4 Sound 11/03/2015 12:42:16 AM 0:00:19 0.0 61.5 70.5 46.2 Sound 11/03/2015 12:44:42 AM 0:00:30 0.0 61.7 72.0 50.6 Sound 11/03/2015 12:45:54 AM 0:00:29 0.0 57.8 67.0 44.1 4 Dakota Aggregates TP2 12am to 2am in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time IN d6j [dBj fdBI Sound 11/03/2015 12:46:57 AM 0:00:16 0.0 61.6 71.1 46.1 Sound 11/03/2015 12:51:51 AM 0:00:30 0.0 62.9 70.6 51.5 Sound 11/03/2015 12:53:46 AM 0:00:25 0.0 60.0 69.2 47.7 Sound 11/03/2015 12:58:01 AM 0:00:30 0.0 66.8 1 80.1 52.0 Sound 11/03/2015 01:04:01 AM 0:00:16 0.0 60.1 67.3 47.7 Sound 11/03/2015 01:05:05 AM 0:00:30 0.0 62.9 73.9 48.7 Sound 11/03/2015 01:07:13 AM 0:00:28 0.0 65.0 76.4 47.8 Sound 11/03/2015 01:07:51 AM 0:00:30 0.0 62.2 69.0 54.6 Sound 11/03/2015 01:10:24 AM 0:00:30 0.0 60.4 69.3 48.8 Sound 11/03/2015 01:11:11 AM 0:00:25 0.0 61.4 1 70.7 45.3 Sound 11/03/2015 01:15:00 AM 0:00:20 0.0 64.4 73.9 44.2 Sound 11/03/2015 01:16:22 AM 0:00:27 0.0 60.9 69.8 48.6 Sound 11/03/2015 01:17:20 AM 0:00:26 0.0 60.1 69.3 48.3 Sound 11/03/2015 01:19:09 AM 0:00:13 0.0 59.9 68.5 46.2 Sound 11/03/2015 01:21:52 AM 0:00:16 0.0 59.3 66.9 46.8 Sound 11/03/2015 01:22:52 AM 0:00:30 0.0 60.9 70.5 48.1 Sound 11/03/2015 01:24:33 AM 0:00.24 0.0 62.1 71.9 45.7 Sound 11/03/2015 01:26:36 AM 0:00:25 0.0 61.4 70.9 46.1 Sound 11/03/2015 01:33:12 AM 0:00:18 0.0 58.0 65.3 46.8 Sound 11/03/2015 01:33:32 AM 0:00:30 0.0 67.5 79.7 47.9 Sound 11/03/2015 01:36:58 AM 0:00:30 0.0 65.1 74.6 49.3 Sound 11/03/2015 01:39:40 AM 0:00:12 0.0 59.51 67.6 44.6 Sound 11/03/2015 01:40:54 AM 0:00:08 0.0 53.9 57.6 46.6 Sound 11/03/2015 01: 41:07 AM 0:00:13 0.0 59.2 65.7 45.5 Sound 11/03/2015 01:41:55 AM 0:00:11 0.0 58.8 65.9 46.8 Sound 11/03/2015 01:44:36 AM 0:00:20 0.0 60.9 70.2 45.7 Sound 11/03/2015 01:45:32 AM 0:00:11 0.01 57.6 63.5 44.8 Sound 11/03/2015 01:46:21 AM 0:00:30 0.0 59.8 71.7 48.2 Sound 11/03/2015 01:47:25 AM 0:00:30 0.0 59.7 71.4 45.9 Sound 11/03/2015 01:52:33 AM 0:00:30 0. 0 61.0 69.9 49.7 Sound 11/03/2015 01:55:00 AM 0:00:21 0.0 59.8 69.7 47.1 Sound 11/03/2015 01:57:02 AM 0:00:23 0.0 62.0 71.2 46.2 Sound 1 11/03/2015 01:58:44 AM 0:00:27 0.0 1 60.81 70.4 45.9 5 0 Dakota Aggregates TP2 12am to 2am in Calculations dB 11/03/2015 12:00:00 AM - 02:00:09 AM Total 100 90--1- 80--l- 0 i- 80 l- 1 _ - - - L - - 70- 60--j- 50 0 60 -i 50 -i- - - - - - - r 30- 20- 10 0 20 10 6.30 16 31.50 63 125 250 500 1000 2000 4000 8000 16000 A L Hz LLeq Cursor: (A) Leq=56.3 dB 6 Dakota Aggregates TP2 12am to 2am in Calculations Based on LAeq, 1s Class width: 1.0 dB 11/03/2015 12:00:00 AM - 02:00:09 AM Total 100 L1 = 68.8 dB L5 = 62.6 dB 90 I - - - 4 L10 = 58.0 dB L50 = 44.8 dB L90 = 34.2 dB80- I - - - - - -1-f- - - - - - + - L95 = 33.1 dBIIIIIII L99 = 30.7 dB 70 - - - - - ,- I- - - - - - r - - - - - -r - - - - - -i I I I I I I I I 60 T -r- - - - - - -r - - - - - - I I I I I I I I 50 I 40 I I I I I I I 30 I I I I I I I 20 I - - - - -'- - - - - - - - - - - - - - - - ! I I I I I I I i 10 I- - - - I I I I 0 20 30 40 50 60 70 80 90 100 dB Level Cumulative Cursor: [50.0 ; 51.0[ dB Level: 3.2% Cumulative: 30.9% 7 Dakota Aggregates TP2 2am to 2:30am in Calculations Event Sound dB 100 j I- - - - - I I 90-- 80- - 70- 60--- 50- - 40-- 30 0 60 - 40- - II I I I I I I 02:00:00 AM 02:05:00 AM 02:10:00 AM 02:15:00 AM 02:20:00 AM 02:25:00 AM 02:30:00 AM LAeq LAFinax Ll-peak LAFmin Cursor: 11/03/2015 02:21:09 AM - 02:21:10 AM LAeq=71.9 dB LAFinax=73.6 dB LLpeak=94.0 dB LAFmin=70.3 dB 1 AErDakota Aggregates TP2 2am to 2:30am in Calculations Name Start Elapsed Overload LAeq LAFinax LAFmin time time dBI fdBIdB Total 11/03/2015 02:00:00 AM 0:30:05 0.0 56.7 77.0 32.0 Unmarked 11/03/2015 02:00:00 AM 0:23:34 0.0 43.6 56.2 32.0 All Event 11/03/2015 02:01:36 AM 0:06:31 0.0 63.2 77.0 42.5 All Sound 11/03/2015 02:01:36 AM 0:04:26 0.0 63.7 77.0 42.5 Event 11/03/2015 02:01:36 AM 0:01:10 0.0 64.1 77.0 46.8 Event 11/03/2015 02:05:49 AM 0:00:41 0.0 60.6 72.0 47.5 Event 11/03/2015 02:11:06 AM 0:00:20 0.0 61.970.2 48.2 Event 11/03/2015 02:17:24 AM 0:00:21 0.0 62.7 73.1 46.8 Event 11/03/2015 02:19:52 AM 0:00:36 0.0 61.6 71.1 45.9 Event 11/03/2015 02:21:03 AM 0:00:27 0.0 62.6 73.6 47.5 Event 11/03/2015 02:22:36 AM 0:00:18 0.0 58.3 66.5 42.5 Event 11/03/2015 02:24:49 AM 0:00:30 0.0 62.6 72.6 48.9 Event 11/03/2015 02:26:29 AM 0:01:22 0.0 63.5 73.9 46.3 Event 11/03/2015 02:28:56 AM 0:00:46 0.0 65.8 76.0 47.7 Sound 11/03/2015 02:01:36 AM 0:00:30 0.0 65.7 77.0 51.7 Sound 11/03/2015 02:05:49 AM 0:00.30 0.0 61.8 72.0 51.7 Sound 11/03/2015 02:11:06 AM 0:00:20 0.0 61.9 70.2 48.2 Sound 11/03/2015 02:17:24 AM 0:00:21 0.0 62.7 73.1 46.8 Sound 11/03/2015 02:19:52 AM 0:00:30 0.0 62.3 71.1 50.0 Sound 11/03/2015 02:21:03 AM 0:00:27 0.0 62.6 73.6 47.5 Sound 11/03/2015 02:22:36 AM 0:00:18 0.0 58.3 66.5 42.5 Sound 11/03/2015 02:24:49 AM 0:00:30 0.0 62.6 72.6 48.9 Sound 11/03/2015 02:26:29 AM 0:00:30 0.0 63.5 72.0 48.6 Sound 11/03/2015 02:28:56 AM 0:00:30 0.0 67.3 76.0 51.4 2 Dakota Aggregates TP2 2am to 2:30am in Calculations dB 11/03/2015 02:00:00 AM - 02:30:05 AM Total 100 I I I 90-1- I 0 i- I - I- i I 70 1 I I I I I I I I I I I i I I I I I I I I I I I I I I I 50--1- - - - - -- I I I I I 40 I I I 30 I I 20--j- I I 10 6.30 16 31.50 63 125 250 500 1000 2000 4000 8000 16000 A L Hz LLeq Cursor: (A) Leq=56.7 dB 3 JAZZ Dakota Aggregates TP2 2am to 2:30am in Calculations Based on LAeq, 1 s Class width: 1.0 dB 11/03/2015 02:00:00 AM - 02:30:05 AM Total L1 = 70.3 dB100 L5 = 62.7 dB 90 I - - - - -I - - - a- - - - - + 4 L10 = 58.6 dB L50 = 41.2 dB L90 = 34.0 dB 80- L95 = 33.5 dB I I I I I I I L99 = 33.0 dB 70 rt - r I I I I I I I I I I I I I I I I 60 -T - T - I NIII50 I- - - - - - - - - I 40 I - - - - I- - - - - - -I 30 I 20- n I I I I I I I 10 I I I I I I I I I 0 20 30 40 50 60 70 80 90 100 dB Level Cumulative Cursor: [50.0 ; 51.0[ dB Level: 2.4% Cumulative: 23.8% 4 a lD v N N H Ill In 0 n N M o0 N m v al " I w W o m H c0 oo lD In lD n m m W lD m H lD lD lD H H H H lD m n V1 V M H 111 H H m m 7 V V Vl V N Vl of n m m V N O oo 6 M N H o o m m o0 o6 v n n n n lD tp lD lD lD lD lD lD lD lD lD lD O' V V lD lD lD lD R to V1 to to to Vl V Vl Ill Vl to to m to to IA Ill Vl V V V V to In lD In In In In In In In v v v v a v v v v v v v v v v v v v v v v v v v v v v v o v v v v v v v v v v v v v v v v m c = C m Ill n n N oo N H n H Vl lD H lD H n m oo w n v lD v V o0 M n n lD V Vl M N N lD n n n n lD In m H m N V M V V o0 oo Ol al N m Hl Ol n In V N oo W Vl n l0 M N H H H O O O m of Ot oo oo n n M n n n n n n n oo oo oo W w w W w W W oo W W w w W w W o0 w w W W W oo W w W m m m W W oo W o6 m n n V V v v V V V V v v M M m M M m M M M M M M M M M M In m M M M m M M M M M M M M M M M M M M M M M M M M M M M M M m M M M M 3 c vp H H o H m In ao o ry m v In vl lD lD lD lD to n oo m o0 w m m m o H N ry N N m m m m v v v v v v v v v o o lD lD lD to n n n n o0 w w n n n n n n f- m ll/ m Ill m Ill ll1 lD to LD lD lD lD lD lD lD lD tD lD lD lD lD lD lD lD to n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n n E c J I x H In y N 01 H v oo oo M N In Ol m o V Ol to f{ H Ol n zt m H n H N M m N n n to V V v Vl Vl Ill Ill V M H Ol oo n Ill V to to lD lD n n n W W n vl M N Vl oo lD M lD In ' D lD c l oo lD 4 M N H O O Ln m v W oo w n n n n n V n n n n n V lD lD lD lD lD lD lD lD lD to lD w Ill Ill Ill o o Ill In Vl Ill Ill Ill Ill to Ill m Ill Ill Ill v v v v to to In In vl In In In In In In v v vvvv v v v v It v v v v v v v v v a v v v v v v v v v v v v v v IT v v v v v v a v v a v aE c H to o o o 0 o o o o o 0 o o 0 o 0 o o o o o o a o o 0 o a o o o o o a o o o o o o 0 0 0 0 0 o o a o 0 o o Cl o o o o o o o o o o o o o oO0 o p ou p O m n n - ztmlD w m m M n In H N m v Ill lD n n 00 w 00 al m w LD 41 00 00 n 00 mN In In v N H N H Ol Dl 1p H N v v lD lD lD to lD Ill v v C Ill In Ill lD n n W tDQ Ol n N M M V d' O In Vl Ill Vl U1 In V1 to In In In In In vl O O V1 Vl In Vl Vl In lD lD wlD lD lD o lD O Vl In O lD lD lD lD wlD lD w wlD lD lD lD tD lD lD l0 l0 lD lD tD O O O O O O O O 0 O O O O O O O O O O O O O O 0 O O O O O O O a a a O O O O O o O O O O O o O O O O O O O O O O O O O O O O O o o o o o o O O O O o a o o o o o o O o O O O o O O o o O O o o O O O o o o O O O O O o o o o o o o o o O O O O O O o Q m p v2 U H O O O O O O O O O O O o o O O O O O O O O O O O O O O O O O O O O O O O O o O O O O O O O o O O O O O O o o O o o O O O O O O O O O 4- a O c LL s N M V n lD m N Q1 n Q1 Vl H 111 n m Ql N N W l0 n al T m v to tD V1 W N O Ill W M H m H M N M Ol H M lD lD Vl Ill m lD W W v v v H V1 m m v M O v H R V to m N N H H H H m m m o Ol m 0 0 O O O O O O O H H H H H H m N N N m M m M m m M N m M M M M M M m M M m V V V v C C m V m m m V V v Ol Ql 41 01 al O1 01 O1 al Ol Ql Ol Ol Ol N Ol Ol Ol 41 Ol m 41 01 O1 Ol Ol 01 < T T Ol m Ol Ol Ol D1 01 01 Ol Cil 01 m Ol 01 Ol Ol Ol Ql Ol al al Ql 01 01 O1 al Ol Ol Ol U Ol Q1 41 41 Ql Ol 01 Ql Ol Ql Ol N Ol Ol Ol Ol Ol Ql 41 Ol Ol al Ql 01 Ol Ol Ol Ol N 01 al N 01 N Q7 N 01 al Ol Ol 01 Ol al al T Ol Ol 01 Ol N M Ol 01 ! 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