23.12.2014 Views

OCTOBER 19-20, 2012 - YMCA University of Science & Technology

OCTOBER 19-20, 2012 - YMCA University of Science & Technology

OCTOBER 19-20, 2012 - YMCA University of Science & Technology

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

Proceedings <strong>of</strong> the National Conference on<br />

Trends and Advances in Mechanical Engineering,<br />

<strong>YMCA</strong> <strong>University</strong> <strong>of</strong> <strong>Science</strong> & <strong>Technology</strong>, Faridabad, Haryana, Oct <strong>19</strong>-<strong>20</strong>, <strong>20</strong>12<br />

[5]. Guite et al.studied the effects <strong>of</strong> urban environment over the public health and well being and they concluded<br />

that the environmental noise can affect the mental health [10].<br />

The major objective <strong>of</strong> the study was to enumerate the spatial and temporal distribution <strong>of</strong> urban traffic noise in the<br />

city <strong>of</strong> Ghaziabad and develop suitable noise maps for evaluation <strong>of</strong> impact.<br />

The investigations were conducted with the intention <strong>of</strong> assessing and quantify the extent <strong>of</strong> road traffic noise<br />

distribution pattern under the urban environment. Following objectives will be attained in this study:<br />

• Improve noise management practices in the study area;<br />

• Assist in planning for upcoming developments in the city;<br />

• Increase awareness among the local population to recognize their existing noise environment and<br />

• The potential for use as an benchmark for other cities, particularly in the Indian subcontinent and elsewhere<br />

to produce city noise maps<br />

2. MATERIALS & METHODS<br />

A. Study area<br />

Ghaziabad, an urban-industrial city and part <strong>of</strong> NCR zone situated in Uttar Pradesh state <strong>of</strong> India, with an area <strong>of</strong><br />

1548 km 2 and a population density <strong>of</strong> 3954/ km 2 has witnessed a sharp growth in vehicular population in the last<br />

five years, ensuing a significant, unrestrained noise pollution across the area The impact identification and<br />

quantification due to such exposure to road traffic noise has been done in such preceding works and it has been<br />

observed that such noise levels in the area are much above the prescribed limits .The situation demands through<br />

investigation, identification and assessment <strong>of</strong> the cause-effect chain due to traffic generated noise exposure. This is<br />

responsible movement <strong>of</strong> heavy and medium vehicles across the main road and throughout the day resulting in high<br />

noise emissions. Regarding to the number <strong>of</strong> vehicles and the traffic load among the rich habitants <strong>of</strong> the NCR region<br />

and by means <strong>of</strong> traffic organization and traffic police center data <strong>of</strong> the mentioned region, the traffic situation and<br />

the number <strong>of</strong> traffic policemen residing in the area were identified and their location were spotted. Then, the places<br />

that the measurement was supposed to carry out were located by means <strong>of</strong> available municipal maps taken from the<br />

traffic organization & from the internet. The traffic volume was assessed in terms <strong>of</strong> Passenger Car Units (PCU). It is<br />

the scale to convert all vehicles into one category, i.e., passenger car. The PCU values for two wheelers, three<br />

wheelers, light commercial vehicles, buses, and heavy commercial vehicles are 0.75, 2, 2.5, 3 and 3, respectively<br />

[16].<br />

B. Data collection<br />

Noise measurement was done at selected locations as shown in fig.1 with the help <strong>of</strong> A digital sound level meter<br />

(IEC651, ANSI S1.4) with frequency range <strong>of</strong> 31.5Hz to 8,000Hz and measuring level range between 35–130 dB<br />

was used for the study. All reading were taken on the ‘A-weighting’ frequency network, at a height <strong>of</strong> about 1.5 m<br />

from ground level and on the ‘Fast’ range time weighting. The ‘A’ weighting characteristic and ‘Fast’ range is<br />

simulated as ‘human ear listening’ response. Sound data were recorded at interval <strong>of</strong> 15 sec for a continuous<br />

sampling period <strong>of</strong> 1 minute during working days and under normal climatic conditions. The data collected from<br />

field were recorded in MS excel worksheet and later transferred to Noise Mapping (Get Data and Surfer) s<strong>of</strong>tware for<br />

further analysis. All noise values were expressed in dB (A) units. For the proper assessment and analysis <strong>of</strong> the<br />

results, the following noise indices were computed: L eq : A-weighted equivalent sound level during sampling period,<br />

L max and L min : Maximum and minimum noise level during sampling period. Equivalent sound level, ‘L eq ’ is<br />

computed using following equation:<br />

N<br />

L eq (dB (A)) = 10 × log 10 [(1/N) ∑i=1 10<br />

Li/10 ] (1)<br />

Where, L i is the noise level <strong>of</strong> the i th reading and ‘N’ denotes total number <strong>of</strong> recorded samples. Such data were<br />

generated for time intervals (8.00 am– 8.00 pm).<br />

766

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!