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FULL PACKET_2005-04-04
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FULL PACKET_2005-04-04
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<br />ALUC Minutes <br />Page 2 <br />January 15, 2004 <br /> <br />CONTINUED BUSINESS: <br /> <br />2. City of Santa Ana - Geneva Commons - MacArthur Place Zone Chanee (JW A AELUP) Gtem <br />continued from December 18,2003): <br /> <br />Executive Officer Golding explained that no replies have been received to the letters sent to ALP A <br />and the FAA, although a verbal contact with the FAA's 7460 specialist revealed that the project is <br />60S' outside ofthe "flight envelope" for instrument approaches to JW A Runway 19R, per the <br />question asked by Commissioner Propst. Ms. Golding next introduced the JW A noise consultant, <br />Mr. Vince Mestre, who presented a noise tutorial at the Commission's request, including the issues <br />of noise impacts at ground level vs. atop high-rise buildings and the effect of proximity to aircraft. <br /> <br />Mr. Vince Mestre, of Mestre-Greve Associates, the contract acoustical consultant for JW A, <br />identified the buildings site at MacArthur Place in relation to the AELUP noise contours from the <br />1985 JW A Master Plan, as well as its distance to aircraft arriving on straight-in and turning <br />approaches to Runway 19R. He next described the slant ranges from the ground and from the top of <br />a 250' proposed building perpendicular to an aircraft on a 30 final approach, and he explained the <br />physics of sound decreasing with distance from the source, such that noise would be .5 dB louder <br />atop the building. However, as described below, he noted that there are numerous other factors <br />which contribute to the actual real world result. When all factors are considered, the noise from a <br />source at a sideline slant range to a site results in a higher noise level at the ground level of the <br />building. <br /> <br />Replying to Commissioners Webb and H. Beverburg, Mr. Mestre noted that the human ear detects a <br />difference of about 3 dB, such that the difference just described is not detectable, adding that other <br />factors affect sound propagation such as ground reflection and bending by temperature inversion and <br />by wind and temperature gradients. He added that empirical data from actual measurements answer <br />such questions. <br /> <br />Mr. Mestre described the reflective qualities of various hard and soft landscape surfaces, noting that <br />research is ongoing into sideline sound propagation as pertains to the FAA's Integrated Noise Model, <br />adding that these issues complicate the correlating of noise model results with actual measurements <br />that are undertaken by airports and aircraft manufacturers. He related the various factors that affect <br />the lateral attenuation and spreading effect vis a vis the ground reflection of noise such as distance, <br />angle to the aircraft, and aircraft size and type, including tail-mounted vs. wing-mounted engines. <br /> <br />Mr. Mestre described the results of calculations for an observer at ground level and on the roof of a <br />250' building, perceiving noise along the slant distances to commercial aircraft arriving straight in to <br />Runway 19R, and his conclusion that it will be noisier on the ground due to the diverse factors <br />affecting sound propagation. He next described the situation of General Aircraft (GA) arriving to <br />19R by flying directly over the building, in which case it would be noisier at the roof than on the <br />ground. The differences for the examples being 3.5 to 4.5 dB respectively, although he opined that <br />actual measurements would likely be less than the model's calculations. <br /> <br />Replying to Commissioner H. Beverburg, regarding such GA operations above the site, Mr. Mestre <br />confirmed that his calculations were all based on A-weighted decibels, to reflect the range of human <br />hearing, and he related the results for various models of GA aircraft affecting a ground level <br />observer. He added that a top-floor observer would, in such examples, likely hear 3 dB more, after <br />describing and comparing the various noise levels to human conversation levels. <br /> <br />75C-165 <br />
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