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Technical sciences 73 THE FACTOR OF NOISE POLLUTION IN THE ORGANIZATION OF THE REST AREAS Zakharov Y.I., Sankov P.N., Zakharov V.Y., Tkach N.A. Prydniprovs’ka State Academy of Civil Engineering and Architecture, Dnepropetrovsk, e-mail: [email protected] The present work is devoted to the assessment of noise pollution in the residential quarter, located in Bolshoye Savino in city of Perm from aircraft Municipal Airport .The authors conducted a quantitative and qualitative assess- ment of the acoustic characteristics of the noise source, represented by fl ying over an aircraft, by theoretical calcula- tions and by the computer simulation and optimization, in accordance with current Russian sanitary regulation for noise. Conducted evaluation of existing sound levels at the objects of protection. Exceeded regulatory allowable values of the expected sound levels at the objects of protection. Developed science-based list of activities for the noise protection of the surveyed objects based on the effectiveness of sound proofi ng. The design of a special noise- reducing hiding areas recreation area in the study area. Keywords: noise characteristics, sources of noise, aircraft, computer simulation, noise protection The present work is devoted to the assess- Materials and methods of research ment of noise pollution in the residential dis- The task of creating an acoustically safe environ- trict, Bolshoye Savino in Perm aircraft from ment of location of population in residential areas of noise the city airport. Considered noise regime of the protection measures was decided on the basis of system territory of the recreation area. approach. Analytical studies were carried out using the methods of applied acoustics, mathematical statistics and Purpose of the study computer simulation. Establishing compliance with the acoustic conditions of stay of people in areas recreation Results of research and their discussion areas located in the area of noise impact of air According to the SN 2.2.4/2.1.8.562-96 transport. The goal is achieved by means of the “Noise at workplaces, in residential and public following tasks: buildings and residential areas” [3] and BNR 1. Identifi cation of the main sources of 23-03-2003 “noise Protection” of the updated noise affecting persons on the territory of the version 2011 [4] the calculation and assess- recreation area of the neighborhood. ment of traffi c noise shall be as the maximum 2. Analytical review of the existing Rus- L sound levels (in dBA) and the equivalent sian system of sanitary, technical and construc- Amax sound levels LAeqv (in dBA) created in our case tion standardization in the fi eld of sound proof- aviation source close to residential areas. ing and confi rmation of the justifi cation of the Rationing is set for regulated intervals day- applicability of these rules of acceptable noise time. Regulated time intervals are 16 hours for local objects. of day time (from 7-00 to 23-00). The main 3. Comparison of analytical results with source of noise presented individual aircraft current Russian sanitary norms of acceptable that are fl ying in the zone of the airport in Perm noise in the territory of the inspected object In the evaluation of community noise to and detecting deviations from them. sanitary and hygienic requirements are gov- 4. Develop a list and focus on practical rec- erned by the maximum permissible noise levels ommendations for sound insulation in case of at rest areas. In Table 1 given the criteria for the exceeding the norms of allowable noise. regulation of noise on areas and rest areas [3]. Table 1 Normalized levels of SN 2.2.4/2.1.8.562-96 (Table 3) [3] for protected areas recreation facilities The sound levels and equiva- Maximum sound The location of the estimated point Time lent sound levels LAeqv dB(A) levels, LAmax dB(A) Recreation area on the territory of daytime 45 60 microdistricts and groups of houses (7:00 to 23:00) EUROPEAN JOURNAL OF NATURAL HISTORY № 6, 2016 74 Technical sciences Prediction of the noise regime of the stud- second and fi fth fl oor at a height of 6 and 17 m ied objects of protection is reduced to the cal- from ground level); culation of sound levels in them on the basis of – on-site residential development at acoustic characteristics of the source Lp, sub- a height of 1,5 m from ground level. ject to the laws of distribution of external noise The estimated model is presented in the in the surrounding development the study area. form of maps of sound fi elds in Fig. 1. Eval- As data input for the acoustic calculation of the uation and review of the noise regime in the accepted value of the measured levels of sound study area taking into account the effect of characteristics of sound sources Lp. aircraft noise in “shelter” are presented be- The above relation is implemented in the low in Tables 1–7. form of a special PC program. With its help From Fig. 1 shows that the expected maxi- estimation, the forecast and the visualization mum levels of external noise in the protected of the noise regime of the investigated ob- area are compared to 71,0 dBA. jects of protection. The estimated models are presented in the form of maps of sound fi elds Estimation of a noise mode in the “shelter” in the following way. The scheme (3D model In the shelter children’s play and recrea- [1, 2]) of the study area shows the sources tion facilities, adopted a pergola of steel frame of noise and objects of protection are placed with cladding made of organic glass (Plexiglas in a Cartesian coordinate system. By calcula- Soudstop) density 1190 kg/m3 thickness of tion and using the results of the instrumental 25 mm. Its space planning solution represented fi eld measurements to determine the levels in Fig. 2. Calculation of airborne sound insu- of the sound source. lation of enclosing structures made of mono- In the second stage estimation the noise re- lithic organic glass (Plexiglas Soudstop) den- gime in the study area carried out the theoreti- sity 1190 kg/m3 25 mm thick and is graphically cal calculation and subsequent visualization of presented in Fig. 2. In all calculation methods sound fi elds indicating the numerical values of are taken from [5]. the expected sound levels in the most typical The calculation of expected sound in- design points that were selected: sulation of the shelter Plexiglas Soud- – the facade of a residential building № 2 stop h = 25 mm, surface mass of material at 2 m from the facade of the building on the m = 29,7 kg/m2: Fig. 1. Map of the sound fi elds of the study area EUROPEAN JOURNAL OF NATURAL HISTORY № 6, 2016 Technical sciences 75 Fig. 2. Scheme plan acoustic cover Built the frequency characteristics of airborne bridged. From point To cut down conducted the sound insulation one Plexiglas Soudstop. Found VA with a slope of 4,5 dB per octave, from point the coordinates of the points B and C at the Table 11 C up held cut a CD with a rise of 7,5 dB per oc- [5]: fB = 17000/25 = 680 Hz; take the next teractive tave. Received broken line ABCD represents the 630 Hz. RВ = 37 dB; fC = 34000/25 = 1360 Hz; frequency characteristic of airborne sound insula- take the next teractive 1250 Hz. RС = 30 dB. Plot- tion of a single layer of Plexiglas Soudstop surface 2 ted on a graph (Fig.3) the points B and C and then density m1 = 25 kg/m . EUROPEAN JOURNAL OF NATURAL HISTORY № 6, 2016 76 Technical sciences Fig. 3. Calculation of airborne sound insulation of enclosing structures made of organic glass (Plexiglas Soudstop) density 1190 kg/m3 25 mm The calculation of expected sound-proof- The acoustic effectiveness of sliding doors ing sliding doors at the entrances to the shelter Calculation of acoustic effi ciency of the Plexiglas Soudstop h = 15 mm, surface mass installation of doors in the shelter of Plexiglas of material m = 17,8 kg/m2. Soudstop 15 mm thick carried out тas follows. Built the frequency characteristics of air- 1. Taken during a full door opening for en- borne sound insulation one Plexiglas Soud- try and exit of people – 20 minutes during the stop. Found the coordinates of the points B and hour in the daytime. C at the Table 11 [5]: fB = 17000/15 = 1133 Hz; 2. It is known that the sum of the two take the next teractive 1250 Hz. RВ = 37 dB; noise levels for a larger correction 0 dB fC = 34000/15 = 2266 Hz; take the next terac- when the difference between folding levels tive 2500 Hz. RС = 30 dB. Plotted on a graph more than 20 dB. In our case, the equivalent (Fig.4) the points B and C and then bridged. noise level in front of the door to the shel- From point To cut down conducted the VA with ter 71 dBA, and the acoustic performance a slope of 4,5 dB per octave, from point C up of the door of Plexiglas Soudstop 15 mm or held cut a CD with a rise of 7,5 dB per octave. 24,3 dB (see Table 3). Received broken line ABCD represents the fre- 3. Calculation of equivalent (by energy) quency characteristic of airborne sound insu- of the noise level in the entrance vestibule lation of a single layer of Plexiglas Soudstop of the shelter after the passage of the door 2 surface density m1 = 15 kg/m . (closed 40 minutes – acoustic effi ciency of EUROPEAN JOURNAL OF NATURAL HISTORY № 6, 2016 Technical sciences 77 24,3 dB and open a 20 – minute acoustic per- ing to known methods applied acoustics gave formance – 0 dBA) will carry out in a known the result 66,2 dB.
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