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HomeMy WebLinkAbout2012-04-17 Planning Board Supplemental Materials (33) Hudson Oesign Groupuc February 27,2012 Bryan Bakis, P.E. SBA Communications Corporation One Research Drive,Suite 200c Westborough, MA 01581 RE: Sprint Vision Cumulative Noise Study Site #: BS23XC422 SBA Site #:MAO 1085-A Site Name:SBA Tower Address:300 Chestnut Street, North Andover,MA 01845 Dear Mr. Bakis: This report is to demonstrate that the project proposed by Sprint is in compliance with the Town of North Andover Zoning By-law requirement Section 8.9(4)(e)(iv) Environmental Standards, and Section 8.9(5)(d)(vi) Noise Filing Requirements. Section 8.9(4)(e)(iv)states: 1. Ground-mounted equipment for wireless service facilities shall not generate acoustic noise in excess of 50dB at the security barrier. In addition,Section 8.9(5)(d)(vi)(c) Requires the equipment to meet The Massachusetts Department of Environmental Protection's (MA DEP) Noise Regulation,310 CMR 7.10. The regulation considers a noise in violation if it: I 1. Increases the broadband sound level by more than 10 dB(A) above ambient, or; 2. Produces a "pure tone" condition-when any octave band center frequency sound pressure level exceeds the 2 adjacent center frequency sound pressure levels by 3 dB(A) or more. I BACKGROUND NOISE SURVEY i HDG performed a background noise survey at the subject property on Saturday February 251h at 8:00 p.m, to Sunday February 26th 8:00 p.m. The logging sound level meter is in conformance with the ANSI S1.4-1983 Type (S)2 & ANSI 51.43-1997 accuracy standards and measurements were taken in accordance with ASTM E 1014-2008 Standard Guide for Measurement of Outdoor A- Weighted Sound Levels. The location of the field measurement is shown on the site plan attached. Table 1 shows the results using the Average Sound Level (Leq) in A-weighted decibels and L90 which is the sound level exceeded 90%of the time (commonly known as the quietist 10%of the time period). L90 allows for filtering of short duration sound sources that produce a higher sound level. p:978.557.5553 f:978.336.5586 a:1600 Osgood Street Building 20 North,Suite 2.101,N.Andover,MA 01845 p:413.588.8139 1:413.517.0590 a:116 Pleasant Street,Ste 302,Easthampton,MA 01027 SprWSieeBS21 Smdy Sprig Sde 0.SI3XG31 Pelle I HDG also calculated the Day-Night Average Sound Level (Ldn). Ldn is the average equivalent sound level over a 24 hour period,with a penalty added for noise during the nighttime hours of 10:00 P.M. to 07:00 a,m. During the nighttime period 10 dB is added to reflect the impact of the noise. Table 1:Summary of Background Noise Data Time Location dB(A) Daytime Le South Fence line 54.4 Evening Le South Fence line 51.9 Entire Period (L9o) South Fence line 49.8 Day-Night Average Ldn South Fence line 58.3 EQUIPMENT NOISE EVALUATION I am well-versed with the technical specifications, published acoustical noise levels, and actual operating conditions of the Alcatel-Lucent 9928 Distributed Base Station (DBS) utilized by Sprint. During normal operating conditions the fresh air cooling fans built into the DBS will create the maximum acoustical noise level of this equipment. in addition,Sprint proposes to remove an existing Lucent Flexent Modcell 2.0 cabinet. Table 2 provides the maximum sound pressure level of the cabinet to be removed and the proposed cabinet. Table 2:Sound Pressure Level at 5' d8 A Flexent Modcell To be Removed 65 AlcateYLucent9928 Pro used 65 ' This sound is approximately equivalent to a standard household vacuum cleaner at 10'. All other proposed equipment does not produce noise during operation. CUMULATIVE NOISE RESULTS Utilizing the free field formula (20 log R) for further attenuation for spherical spreading we show the calculated noise levels in Table 3. Table 3: Calculated Sound Pressure Levels Entire Period Day-Night Average i LPo MA DEP Ldp N.Andover Sound Pressure Level of Alcatel-Lucent 9928 (dB(A)) 65.0 65.0 Sound Pressure Level of Flexent Modcell (to be removed) 65.0 65.0 ` (dB(A)) Net Change (dB(A)) 0.0 0.0 Background Noise at the Security Fence from Table 1 (dB(AL 49.8 58.3 Horizontal Distance to Nearest Property Line Feet+/- 70 70 Calculated SPL at Property Line (dB(A)) 26.9 35.4 Increase in$ack round Noise at the Property Line(dB(A)) 0.0` Increase in background noise at the Security Fence to the 0.0" south (dB(A)) I p:413.588.6139 1;413.517.0590 a:116 Pleasant Street,Ste 302,Easthampton,MA 01027 p:978.557.5553 f:978.336.5586 a:1600 Osgood Street,Building 20 North,Suite 2.101,N.Andover,MA 01845 I C4.IltfiY N06e SNdy SPIN She DS23XC422 P+1e1 `Note: Sprint is proposing to replace the existing Flexent Modcell cabinet with the new 9928 DBS with a similar acoustic noise level of 65 dB(A). Therefore it is anticipated that there will be no change in the background noise levels at the fence and property lines. CONCLUSION The Town of North Andover defines a noise in violation if it exceeds 50 dB at the security barrier. The Average Day-Night noise level (Ldn) is estimated to be 58.3 dB(A). However,Sprint proposes to remove an existing Lucent Flexent Modcell 2.0 cabinet which produces a similar sound pressure level as the proposed Alcatel-Lucent 9928. As a result, there will be no perceptible change in noise at the security fence or the properly line. The MA DEP Noise Regulation,310 CMR 7.10 defines unnecessary, excessive, or offensive noise as a noise level which exceeds the ambient noise level by 10 dB(A),and 3 dB(A) if a tonal component exists. There is no calculated increase in the noise level at the south property line. Therefore, during normal operating conditions, it is my professional opinion that the predicted maximum acoustical noise levels from the Sprint equipment will be in conformance with the MA DEP noise regulation. Sincerely, `�,oA�t'AOF6ta 9cy o DERE 1C 11. t� IV o. tg5 Derek J. Creas Sr. Project Manager I I i I� i i 3 i p:970.557.5553 (:978.336.6586 0:1600 Osgood Street,Building 20 North,Suite 2.101,N.Andover,MA 01845 p:413.668.813? 1:413.517.0590 a:116 Pleasant Sfreet,Ste 302,Easlhampion,MA 01027 Spriint> SBATDD�D� ., 70'+/ to closest '�' propert line to the south Hudson +a` w. + ., o..w ouc o ` S i O Gin M ti @ .0.470 SOURCE: W,111 ��1 I\ SITE SPECIFIC NOTES: ,.art wwn.a.m m maum n.vu _ ZONING INFORMATION ewm.iuv.m,a va.m '. ornm� Y..W awr xmu. rr n, ax. Mraom m: ae ' mxnw. x >w. +m. SUBMITTALS / Approximate .wr..n location of Noise �"- Meter TlypOVMe �VM,M/Wb,w t0, M 9 r j � I 4V@.'Lw LEGEND i w,w j SS23XC422 =roof: SBA TOWER ANTENNA ORIENTATION KEY �0°�"�^"rr�. I wan,.xoovm. o,eo NCr SEVT�R PLOT PIAN k4klqlllt PLOT PLAN a dB 66- 64- 62- 'k 66462 'k it I-Aeq 60- 58 56 54 � 9 p i 52 ,I 1 50 � � ' � i � � � � LAF90.0% 1 i LL 1 111 (I� 48 46 18:00:00 00:00:00 06:00:00 12:00:00 18:00:00 02/25/2012 Time C:\users\dcreaser\desktop\run indigo (2) .dta Overall profile duration = 28:25:00 (1705 samples) Cursor:1:::Time =+r 02/25/2012.,22:00:10, Level = 49.5, 48.5 dB, Flags: ----- Cursor 2: Time'= 02/26/2012 07:00:10, Level = 51.4, 49.0 dB, Flags: ----- Duration on / between the cursors = 09:01:00, Flags: UO---, Scale: 1:1, Threshold: 0 dB - LI - Time at or above 0 dB = 28:25:00, overall Time at or above 0 dB = 09:01:00, on / between the cursors Time at or above 0 dB = 19:24:00, outside the cursors Time below 0 dB = 00:00:00, overall Time below 0 dB = 00:00:00, on / between the cursors Time below 0 dB = 00:00:00, outside the cursors Maximum LAeq = 61.7 dB, Time of maximum = 02/25/2012 22:25:10, on / between the cursors Minimum LAeq = 47.1 dB, Time of minimum = 02/25/2012 23:02:10, on / between the cursors Calculated average LAeq = 53.7 dB, overall, (Threshold = 0 dB) Calculated-average::LAeq -=-51.9 dB, . on ./:between-the cursors,...(Threshold-= .0 dB) Calculated average LAeq = 54.4 dB, outside the cursors, (Threshold = 0 dB) Calculated SEL = 103.8 dB, overall, (Threshold = 0 dB) Calculated SEL = 97.0 dB, on / between the cursors, (Threshold = 0 dB) Calculated SEL = 102.8 dB, outside the cursors, (Threshold = 0 dB) Calculated Lep,d = 59.2 dB, overall, (Threshold = 0 dB) Calculated Lep,d = 52.4 dB, on / between the cursors, (Threshold = 0 dB) Calculated Lep,d = 58.2 dB, outside the cursors, (Threshold = 0 dB) - LAF90.0% - Time at or above 0 dB = 28:25:00, overall Time at or above 0 dB = 09:01:00, on / between the cursors Time at or above 0 dB = 19:24:00, outside the cursors Time below 0 dB = 00:00:00, overall Time below 0 dB = 00:00:00, on / between the cursors Time below 0 dB = 00:00:00, outside the cursors Maximum LAF90.0% = 55.5 dB, Time of maximum = 02/26/2012 03:32:10, on / between the cursors Minimum LAF90.0% = 46.5 dB, Time of minimum = 02/25/2012 22:57:10, on / between the cursors Calculated average LAF90.0% = 49.0 dB, on / between the cursors dB 66- 64- 1 I 62 LAeq 60- 58 0 58 i q ' 56-1 I � 54 52 50 LAF90.0%II �II jMI IIII14 ' II lil II ��III �11 ' �' ;1 �IIII:g311111II II I II li I I I �I� � IJ II III i IIP I� O �� I I 48 46 18:00:00 00:00:00 06:00:00 12:00:00 18:00:00 02/25/2012 Time C:\users\dcreaser\desktop\run indigo (2) .dta Overall profile duration = 28:25:00 (1705 samples) Cursor-1: ..Time :=:-02/.25/2012 -19:58:10, Level = 50.5, 49.0 dB, Flags: ----- Cursor 2: Time 02/26/2012 19:58:10, Level = 47.3, 47.0 dB, Flags: ----- Duration on / between the cursors = 24:01:00, Flags: UO---, Scale: 1:1, Threshold: 0 dB - LI - Time at or above 0 dB = 28:25:00, overall Time at or above 0 dB = 24:01:00, on / between the cursors Time at or above 0 dB = 04:24:00, outside the cursors Time below 0 dB = 00:00:00, overall Time below 0 dB = 00:00:00, on / between the cursors Time below 0 dB = 00:00:00, outside the cursors Maximum LAeq = 62.6 dB, Time of maximum = 02/25/2012 21:10:10, on / between the cursors Minimum LAeq = 47.1 dB, Time of minimum = 02/25/2012 23:02:10, on / between the cursors Calculated average LAeq = 53.7 dB, overall, (Threshold = 0 dB) Calculated average LAeq = 52.3 dB, on / between the cursors, (Threshold = 0 dB) Calculated average LAeq = 57.7 dB, outside the cursors, (Threshold = 0 dB) Calculated SEL = 103.8 dB, overall, (Threshold = 0 dB) Calculated SEL = 101.7 dB, on / between the cursors, (Threshold = 0 dB) Calculated SEL = 99.7 dB, outside the cursors, (Threshold = 0 dB) Calculated Lep,d = 59.2 dB, overall, (Threshold = 0 dB) Calculated Lep,d = 57.1 dB, on / between the cursors, (Threshold = 0 dB) Calculated Lep,d = 55.1 dB, outside the cursors, (Threshold = 0 dB) - LAF90.099 - Time at or above 0 dB = 28:25:00, overall Time at or above 0 dB = 24:01:00, on / between the cursors Time at or above 0 dB = 04:24:00, outside the cursors Time below 0 dB = 00:00:00, overall Time below 0 dB = 00:00:00, on / between the cursors Time below 0 dB = 00:00:00, outside the cursors Maximum LAF90.09s = 59.5 dB, Time of maximum = 02/25/2012 21:10:10, on / between the cursors Minimum LAF90.0% = 46.5 dB, Time of minimum = 02/25/2012 22:57:10, on / between the cursors Calculated average:LAF90.0% = 49.8 dB, on / between the cursors Community Noise Calculators-Ldn, Lden and CNEL Page 1 of 1 Home Contact Products Hire Calibration�Survey� Nevis Resources Help Search Carttin Home>Apps>Ldn Calculator Tel. 0845 680 0312 info@nolsomotors.co.uk Ldn, Lden, CNEL -Community Noise Calculators Ldn and Lden Calculator Ldn and Lden Calculator Start Hourly CaICOiate:. Calculation of the Ldn(day,night)and the Lden(day,evening, ' Time Leq night)based on 1-hour Leq measurements. Calculators 00:00 52.0 as ✓ Ldn -Day Night Average Sound Level 01:00 519; da ✓. Leq 02:0049.5'. de f.. 62.3 dB The Ldn is the average equivalent sound level over a 24 hour period,with a 03:00 52.61 ds V penalty added for noise during the nighttime hours of 22:00 to 07:00.During the 04:00 52.81 de tJ Ldn nighttime period 10 dB is added to reflect the impact of the noise. 05:00 508', de 58.3 d6 Ldn measurements are useful for assessing the impact that road,rail,air and 06:00 - 50.7''. da f general Industry has on the local population. 07:00 503 dB f Lden 08:00 466'.. de V 58.6 dB The NoiseMelers Ldn calculator accepts hourly Leq measurements and calculates 09:00 49.71. dB I/ the Ldn accordingly. 10:00 sob' de V Lden or CNEL 11:00 50.i;! dB f 12:00 53.6'I dB ./. The Lden(Day Evening Night Sound Level)or CNEL(Community Noise 13:00 54.4'.. dB ,J Equivalent Level)is the average sound level over a 24 hour period,with a penalty 14:00sa.al de �!` of 5 dB added for the evening hours or 19:00 to 22:00,and a penalty of 10 dB added for the nighttime hours of 22:00 to 07:00. 15:00 54.61 dB .j 16:00 54511 dB .j' It is very similar in nature(and in results)to the Ldn,but with the added penalty for 17:00 52.5 dB the evening period. 18:00 47.6j dB Our Lden or CNEL calculator takes the hourly Leq measurements and calculates 19:00 : 47.7' de ,/ the Lden(which is the same as the CNEL). 20:00 '1 53.4 dB .f 21:00 55.91 dB ./ 22:00 53.0j dB vP 23:00 50.E de <Noise Applications Home-Contact-News-Rental-Survey-Calibration-Resources-Search-Help Telephone 0845 680 0312 General Purpose-Signs-Noise at Work-Environmental-Accessodes-Mobile Site RHP ; ,. info@noisemeters.co.uk http://www.noisemeters.co.uk/apps/idn-calculator/ 2/27/2012 Basic site preparation requirements and footprints for 9928 Environmental requirements t: Distributed Base Station outdoor cabinet Site requirements for 9928 Distributed Base Station e. .066 cab'IneY.. ............... ... ......................................................................................................................................,.......... 0 nvironmental requirements Environmental requirements for outdoor installations Outdoor cabinet installations are exposed to variations in temperature,humidity,and r, ventilation. The 9928 Distributed Base Station cabinet has been weather-hardened. When equipped { with a heat exchanger,the cabinet will operate under the conditions described in the table below. Condition Specification Operating -40°C to+46°C(40 OF to+115 °F) temperature Extended operating -40°C to 50°C(40 OF to 122°F) temperature Relative humidity 5 to 100%(non-condensing but not to exceed 0.024 kg tvater/kg of dry air) Enclosure rating Type 3R(NEMA) IP35 (IEC 60529) Acoustic noise 65 dBA at 25°C(77°F)and sea level suppression Operating altitude -60.96 to 1798 n1(-200 to 5,900 ft.)above sea level Extended operating -60.96 to 3048 m(-200 to 10,000 ft.).An operating temperature altitude de-rating of 1 °C per 1000 feet above 6000 feet is allowed Wind driven rain Refer to Telcordia GR-487-CORE Dust and water Refer to Telcordia GR-487-CORE ingress Bullet resistance Refer to Telcordia GR-487-CORE Wind resistance Refer to Telcordia GR-487-CORE Storage requirements Refer to Telcordia GR-63-CORE, Section 4.1.1 ............................................................................................................................ ........ .......................................................................................... 9928 Dist BTS outdoor Alcatel-Lucent-Proprietary 5.5 401-703-732FOA Issue 1 Draft 9 Use pursuant to applicable agreements September 2011 ,.:.' Lucent Technologies WLt. ,0 Network Systems- Product Realization Center subject: Bellcore Requirement GR-487-CORE slate: April 5,2000 Section 3.28 Requirement R3-157 Acoustical Noise Suppression Test Report For the Flexent outdoor version Modcell(Cellular and PCS) from: Stephen Baroczi Org.JW 112AO02 NJ0452, 1G3M (973)426-1396 !sbaroczi@lucent.com Memorandum for Record Introduction The Acoustical Noise Suppression test was performed on an outdoor version Flexent Modcell on January 24,2000 at the Noise Unlimited Inc.test laboratory located in Annandale,NJ.This test was conducted to verify compliance of the outdoor version of the Flexent Modcell to the Bellcore acoustic noise suppression requirement specified in section 3.28 R3-157 of GR-487-CORE(Generic Requirements for Electronic Equipment Cabinets)see Noise Unlimited Test Report No.9065.1.Marvin Lowman of Noise Unlimited Inc.conducted the testing.G.Mikus and J.Stofanek of Lucent Technologies were present during the testing. Bellcore Requirement Description Cabinets,equipped with telecommunications equipment and associated cooling falls,shall suppress acoustical noise to a level of 65dBA at a distance of 1.5nh(5ft)from the cabinet with the doors closed during times of maximum noise generation within the cabinet. Test Procedure: • Sound measurements shall be made in a room or enclosure that duplicates as much as possible the acoustic properties of a network facility and the actual service environment. • The sound level shall be measured by a sound meter meeting ANSI 1.4,and set to the A- weighting scale and the slow meter response setting. • Measurements shall be made in accordance with ANSI St.18. • Cabinet doors shall be closed. • Sound levels produced shall be measured at 5ft from the cabinet surfaces in all horizontal directions at a height of 3ft from the cabinet mounting surface. Test Setup Lucent Technologies Proprietary-Use pursuant to Company Instructions e) Environmental Standards i) Wireless services facilities shall not be located in wetland resource areas. Locating of wireless facilities in wetland buffer areas shall he avoided whenever possible and disturbance to wetland buffer areas shall be minimized. All Conservation Commission regulations and procedures must be followed. ii) No hazardous waste shall be discharged on the site of any personal wireless service facility. If any hazardous materials are to be used on site, there shall be provisions for full containment of such materials. An enclosed containment area shall be provided with a sealed floor, designed to contain at least I10%of the volume of the hazardous materials stored or used on site.Applicant must comply with all federal, state and local regulations governing hazardous materials. iii) Storm water run-off as a result of the wireless facility shall be contained on-site and comply with the DEP Storm Water Management regulations as applicable. iv) Ground-inounted equipment for wireless service facilities shall not generate acoustic noise in excess of 50 dB at the security barrier. v) Roof-mounted or side-mounted equipment for wireless service facilities shall not generate noise in excess of 50 dB at ground level at the base of the building closest to the antenna. Safety Standards i) Radiofrequency Radiation (RFR) Standards.All equipment proposed for a wireless service facility shall be authorized per the FCC Guidelinesfor Evaluating the Environmental Effects of Radiofrequency Radiation (FCC Guidelines)or any other applicable FCC guidelines and regulations. ii) Structural Integrity. The applicant shall provide certification by a structural engineer that the wireless set-vice facility is structurally sound for the proposed facility. 5) Application Procedures a) Special Permit Granting Authority, (SPGA). The Special Permit Granting Authority (SPGA) for wireless service facilities shall be the Planning Board. b) Pre-Application Conference. Prior to the submission of an application for a Special Permit under this regulation, the applicant is strongly encouraged to meet with the SPGA at a public meeting to discuss the proposed wireless service facility in general terms and to clarify the filing requirements. c) Pre-Application Conference Filing Requirements. The purpose of the conference is to inform the SPGA as to the preliminary nature of the proposed wireless service facility. As such, no formal filings are required for the pre-application conference. However, the applicant is encouraged to prepare sufficient preliminary architectural and/or engineering drawings to inform the SPGA of the location of the proposed facility, as well as its scale and overall design. d) Application Filing Requirements.The following shall be included with an application for a Special Permit for all wireless service facilities: i) General Filing Requirements (1) Name, address and telephone number of applicant and any co-applicants as well as any agents for the applicant or co-applicants. A 24-hour emergency telephone contact number shall be included for use during construction as well as operation of the wireless communication facility. (2) Co-applicants may include the landowner of the subject property, licensed carriers and tenants for the wireless service facility (3) Every application for a wireless service facility Special Permit shall include at least one licensed carrier and the owner of the land as an applicant or a co-applicant. 99 foot-candle levels at grade, within the property to be developed and twenty-five (25) feet beyond property lines. The printout shall indicate the locations and types of luminaries proposed. vi) Noise Filing Requirements (1) The applicant shall provide a statement listing the preexistent and maximum future projected measurements of noise from the proposed wireless service facilities, measured in decibels Ldn(common logarithmic scale,accounting for greater sensitivity at night), for the following: (a) Preexistent or ambient: the measures of preexistent noise (b) Preexistent plus proposed wireless service facilities: maximum estimate of noise from the proposed wireless service facility plus the preexistent noise environment. (c) Such statement shall be certified and signed by an acoustical engineer, stating that noise measurements are accurate and meet DEP requirements and Section 8.9(4)(e). vii)Radiofrequency Radiation (RFR)Filing Requirements (1) All telecommunications facilities shall be operated only at Federal Communications Commission(FCC) designated frequencies, power levels and standards, including FCC Radio Frequency Emissions standards. The applicant shall provide certification demonstrating that the maximum allowable frequencies; power levels will not be exceeded. Certifications shall include technical specifications, a written explanation of those specifications, and, if necessary, field verification. The Permit Granting Authority may condition any Special Permit granted under this section upon a periodic submittal of certification of compliance with said standards. (2) In order to determine compliance with applicable FCC regulations, the applicant shall provide a statement listing the preexistent and maximum future projected measurements of RFR from the proposed wireless service facility, including all co- locators, for the following situations: (a) Preexistent or ambient: the measurement of preexistent RFR. (b) Preexistent plus proposed wireless service facilities: maximum estimate of RFR from the proposed wireless service facility plus the preexistent RFR environment. (c) Certification, signed by a engineer, stating that RFR measurements are accurate and meet FCC Guidelines as specified in the Radiofrequency Radiation Standards subsection of this Bylaw. (3) Applicant must submit a copy of the letter from the Massachusetts Department of Public Health approving the site for this facility as required by 105 CMR 122.000 requires that the Department of Public Health approve all sites for wireless facilities with respect to emissions. viii) Federal Eiivirmrrnental Filing Requirements (1) At the time of application filing, an Environmental Assessment (EA)that meets FCC requirements shall be submitted to the Town for each wireless service facility site that requires such an EA to be submitted to the FCC (2) The applicant shall list location, type and amount(including radiation trace elements) of any materials proposed for use within the wireless service facility that are considered hazardous by the federal, state or local government. ix) Waiver. The SPGA may waive one or more of the application filing requirements of this section if it finds that such information is not needed for a thorough review of a proposed personal wireless service facility. 6) Co-location a) Licensed carriers shall share wireless service facilities and sites where feasible and appropriate, thereby reducing the number of wireless service facilities that are stand-alone 102 fact sheet Noise Background M a s s a c n u s a 1 , $ Noise is a type of air pollution that results from sounds that cause a D o p a r t m a n t nuisance, are or could injure public health, or unreasonably interfere with ENVIRONMENTAL the comfortable enjoyment of life, property, or the conduct of business. P R O T E C T I O N Types of sounds that may cause noise include: • "Loud" continuous sounds from industrial or commercial activity, demolition, or highly amplified music; • Sounds in narrow frequency ranges such as "squealing" fans or other rotary equipment; and • Intermittent or"impact" sounds such as those from pile drivers, jackhammers, slamming truck tailgates, public address systems, etc. Policy A noise source will be considered to be violating the Department's noise regulation (310 CMR 7.10) if the source: Massachusetts Department of 1. Increases the broadband sound level by more than 10 dB(A) Environmental Protection above ambient, or One Winter Street 2. Produce a "pure tone" condition —when any octave band center Boston,MIA 02108-4746 frequency sound pressure level exceeds the two adjacent Commonwealth of center frequency sound pressure levels by 3 decibels or more. Massachusetts These criteria are measured both at the property line and at the nearest Mitt Romney,Governor inhabited residence. "Ambient" is defined as the background A-weighted Executive Office of sound level that is exceeded 90% of the time, measured during Environmental Affairs equipment operating hours. "Ambient" may also be established by other Ellen Roy Herzfelder,Secretary means with consent of the Department. Department of For more information: Environmental Protection For complaints about specific noise sources, call the Board of Health for Edward P.Kunce, the municipality in which the noise source is located. Acting Commissioner To learn more about responding to noise, odor and dust complaints or to request state assistance or support, please contact the service center in Produced by the the nearest DEP regional office. Bureau of Waste Prevention February 2003. • Central Region, Worcester: (508) 792-7683 Printed on recycled paper. • Northeast Region, Wilmington: (978) 661-7677 • Southeast Region, Lakeville: (508) 946-2714 This information is available in • Western Region, Springfield: (413) 755-2214 alternate format by calling our ADA Coordinator at This Policy was originally adopted by the MA Department of Public Health in the early (617)574-6872. 1970s. It was reaffirmed by DEP's Division of Air Quality Control on February 1, 1990, and has remained in effect. noisefs•Page 1 of 1