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Example Problem 14-2 The following sound exposure levels for four aircraft flyovers were measured in a 1-h period: 840, 891, 902, and 866 dB To compute the hourly average sound level, we must substitute into Eq (14-7) obtaining 1 Leq = 10 log (1084 0/10 + 1089 1/10 + 1090 2/1 0 + 1086 6/10 ) 3600 = 10 log 713 339 58 5 dB

Try this query twice First, run the whole query Then, highlight everything except the Where clause and run the query again

# operator, 199 %# character, 130 %~ character, 130 %> character, 130 %/ character, 130 %M character, 130 %m character, 130 %n character, 130 % operator, 199, 203 %R character, 130 %:variable character, 130 & operator, 199 * operator, 203 @ operator, 199 ^a symbol, 201 ^ operator, 199 _ operator, 203 ||/ operator, 199 | operator, 199 |/ operator, 199 !~* operator, 200 ~* operator, 200 !~ operator, 200 ~ operator, 200 + operator, 199, 203 << operator, 199 <= operator, 200 <> operator, 200 < operator, 200 = operator, 199, 200 != operator, 200 >= operator, 200 >> operator, 199 > operator, 200

It will be observed that even though the sound exposure level of each aircraft flyover was greater than 585 dB the averaging process reduces the hourly average sound exposure level

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Experience has shown the concept of an average sound level is often misinterpreted by the affected public as an underreporting or understatement of their noise environment Their concern is that the metric does not report the total noise energy over the time period As can be seen in Eqs (14-5), (14-6), and (14-7), this metric, as well as other average metrics, does indeed include all of the noise energy Each and every noise event, no matter how high or low the sound level, increases the value of the metric Viewed another way, the average value is the total noise energy adjusted by a constant, 10 log T The local community component of the equivalent steady sound level is also a frequently reported statistic which serves as a basis of comparison for the aircraft component It may be estimated using a variant of Eq (14-6) which accumulates sound levels only during subintervals of the total period when no aircraft are present It is an estimate because there is no way of knowing the community sound level contribution during periods when aircraft are present Equation (14-8) shows the basic summation process Each summation in the equation represents a nonaircraft subinterval

Nn N2 1 N1 Leq = 10 log 10 L A ,i /10 + 10 L A ,i /10 + + 10 L A ,i /10 (14-8) N i=1 i=1 i=1

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LA,i = instantaneous ith A-weighted sound level measured every 05 s N1, N2, Nn = number of sound level samples in each subinterval containing no aircraft noise N = total number of samples which is equal to (N1 + N2 + + Nn)

This metric is referred to as the hourly average sound level when 1 h of averaging time is used (Although not meeting current acoustical terminology standards, the hourly average sound level may be reported in the literature as the hourly noise level, HNL, hourly Leq or 1-h Leq) In airport applications, hourly average sound levels may be used for plotting and visualizing diurnal trends Eight and twenty-four hour periods are referred to as 8-h and 24-h average sound levels The symbol Leq is generic referring to any arbitrary period of time To avoid ambiguity, the subscript is replaced by the appropriate time frame Thus, the symbols L1 h, L8 h, and L24 h, are used for 1-, 8-, and 24-h periods, respectively

It doesn t matter whether or not you include the Where clause when it contains only a default member (measure or attribute) The two queries have identical outcomes Notice the cell values before you attempt the ensuing query

As the name implies, the day-night average sound level, DNL, is a metric used to describe sound exposure over a 24-h period and the units

a$ symbol, 201 a* symbol, 201 a|b symbol, 201 a+ symbol, 201 [a-b] symbol, 201 [abc] symbol, 201, 203 ABORT keyword, 145 About tab, 270 ABSOLUTE count option, 191 abs(x) function, 212 Access See Microsoft Access and PostgreSQL Accountant group, 108 112

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