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Section 4.0 — Environmental Setting and Discussion of Impacts <br />4.12 NOISE <br />4.12.1 Background Information <br />4.12.1.1 Fundamentals of Norse <br />Noise is defined as unwanted sound. Sound levels are usually measured in decibels (dB) with 0 dB <br />corresponding roughly to the threshold of hearing, Most of the sounds which we hear in the <br />environment do not consist of a single frequency, but rather a broad band of frequencies, with each <br />frequency differing in sound level. The intensities of each frequency add together to generate a <br />sound. The method commonly used to quantify environmental sounds consists of evaluating all of <br />the frequencies of a sound in accordance with a weighting that reflects the fact that human hearing is <br />less sensitive at low frequencies and extreme high frequencies than in the frequency mid-range. This <br />is called "A" weighting, and the decibel (dB) level so measured is called the A -weighted sound level <br />(dBA). In practice, the level of a sound is conveniently measured using a sound level meter that <br />includes an electrical filter corresponding to the A -weighting curve. <br />Although the A -weighted noise level may adequately indicate the level of environmental noise at any <br />instant in time, community noise levels vary continuously. Most environmental noise includes a <br />conglomeration of noise from distant sources which create a relatively steady background noise in <br />which no particular source is identifiable. To describe the time -varying character of environmental <br />noise, the statistical noise descriptors, Lot, Lto, L5o, and Loo, are commonly used. They are the A - <br />weighted noise levels equaled or exceeded during 1, 10, 50, and 90 percent of a stated time period. A <br />single number descriptor called the Leq is also widely used. The Lcq is the average A -weighted noise <br />level during a stated period of time. <br />In determining the daily level of environmental noise, it is important to account for the difference in <br />response of people to daytime and nighttime noises. During the nighttime, exterior background <br />noises are generally lower than daytime levels. Most household noise, however, also decreases at <br />night and exterior noises become more noticeable. Further, most people sleep at night and are very <br />sensitive to noise intrusion. To account for human sensitivity to nighttime noise levels, a descriptor, <br />DNL (day/night average sound level), was developed. The DNL, or Ld„ divides the 24-hour day into <br />the daytime of 7:00 AM to 10:00 PM and the nighttime of 10:00 PM to 7:00 AM, The nighttime <br />noise level is weighted to 10 dB higher than the daytime noise level to account for the increased <br />noise sensitivity. The Community Noise Equivalent Level (CNEL) is another 24-hour average which <br />includes both an evening and nighttime weighting. <br />4.12.1.2 Fundamentals of Vibration <br />Ground vibration consists of rapidly fluctuating motions or waves with an average motion of zero. <br />This discussion uses Peak Particle Velocity (PPV) to quantify vibration amplitude, which is defined <br />as the maximum instantaneous positive or negative peak of the vibration wave. A PPV descriptor <br />with units of millimeters per second (mm/sec) or inches per second (in/sec) are used to evaluate <br />construction generated vibration for building damage and human complaints. The two primary <br />concerns with construction -induced vibration are the potential to damage a structure and the potential <br />City of Redwood City 71 Initial Study/Mitigated Negative Declaration <br />Sandpiper Elementary School Facilities Expansion November 2016 <br />