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Environmental propagation of noise in mines and nearby villages: A study through noise mapping

机译:矿山和附近村庄中噪声的环境传播:通过噪声映射的研究

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Background: Noise mapping being an established practice in Europe is hardly practiced for noise management in India although it is mandatory inIndian mines as per guidelines of the Directorate General of Mines Safety (DGMS). As a pilot study, noise mapping was conducted in an opencastmine with three different models; one based on the baseline operating conditions in two shifts (Situation A), and two other virtual situations whereeither production targets were enhanced by extending working hours to three shifts (Situation B) or only by increased mechanization and notchanging the duration of work (Situation C). Methods: Noise sources were categorized as point, line, area, and moving sources. Consideringmeasured power of the sources, specific meteorological and geographical parameters, noise maps were generated using Predictor LimA software.Results: In all three situations, Lden values were 95 dB(A) and 70–80 dB(A) near drill machine and haul roads, respectively. Noise contourswere wider in Situation C due to increase in frequency of dumpers. Lden values near Shovel 1 and Shovel 2 under Situation B increased by 5 dBand 3 dB, respectively due to expansion of working hours. In Situation C, noise levels were >82 dB(A) around shovels. Noise levels on both sidesof conveyor belts were in the range of 80–85 dB(A) in Situations A and C whereas it was 85–90 dB(A) in Situation B. Near crusher plants, itranged from 80 to 90 dB(A) in Situations A and C and between 85 and 95 dB(A) in Situation B. In all situations, noise levels near residential areasexceeded the Central Pollution Control Board (CPCB) limits, i.e., 55 dB(A). Conclusions: For all situations, predicted noise levels exceededCPCB limits within the mine and nearby residential area. Residential areas near the crusher plants are vulnerable to increased noise propagation. Itis recommended to put an acoustic barrier near the crusher plant to attenuate the noise propagation.
机译:背景:尽管根据矿山安全总局(DGMS)的指南,印度的矿山必须进行噪声测绘,但在欧洲几乎没有将噪声测绘作为欧洲的一项常规做法。作为一项试点研究,在具有三种不同模型的露天矿中进行了噪声映射。一种基于基线工作条件(两班制)(情况A),另一种基于虚拟情况,通过将工作时间延长至三班制(方案B)或仅通过增加机械化程度和不改变工作时间来提高生产目标(方案C) )。方法:噪声源分为点,线,面和移动源。考虑到源的测量功率,特定的气象和地理参数,使用Predictor LimA软件生成了噪声图。结果:在所有三种情况下,钻机和运输道路附近的Lden值分别为95 dB(A)和70–80 dB(A)。 , 分别。由于倾销者频率的增加,情况C中的噪声等值线变宽。由于工作时间的延长,情况B下的1号铁锹和2号铁锹附近的Lden值分别增加了5 dB和3 dB。在情况C中,铁锹周围的噪音水平> 82 dB(A)。在情况A和情况C下,传送带两侧的噪音水平在80-85 dB(A)的范围内,而在情况B下则在85-90 dB(A)的范围内。在破碎机厂附近,噪音水平在80至90 dB(A)范围内。情况A和C,情况B在85至95 dB(A)之间。在所有情况下,居住区附近的噪声水平均超过中央污染控制委员会(CPCB)的限制,即55 dB(A)。结论:在所有情况下,矿山和附近居民区内的预测噪声水平均超过了CPCB限制。破碎机厂附近的居民区容易受到噪声传播的影响。建议在破碎机附近放置一个声屏障,以降低噪声传播。

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