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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2096
Prediction of noise levels using FHWA Model for National highway 150
A (NH 150-A)
Sagar Pashupatihal, Sneha R, Sumanth K
1(Dept. of Environmental Engineering, Manipal Institute of Technology, Manipal, India)
2(Dept. of Civil Engineering, Manipal Institute of Technology, Manipal, India)
3(Senior highway Engineer, C V Kand Consultants Pvt. Ltd, Bengaluru, India)
---------------------------------------------------------------------***---------------------------------------------------------------------
Abstract - Population growth and developmentofactivities
in cities have a great influence on the development of
transportation sector. The high growthrateofprivatevehicles
is mainly due to increase in the population. This condition has
enlarged environmental degradation, not only in terms offuel
consumption but also in terms of air pollutionandtrafficnoise
generated by vehicles. Noise generated by traffic is having
many adverse effects such as increase of stress, sleep
disturbance, communication difficulty and also hearing
problem. In order to overcome these problems, itisrequiredto
estimate the level of traffic noise produced by traffic volume
and average speed of the vehicles. In the present work, the
traffic noise along a highway corridor on NH-150A passing
through Nanjanagudu city of Mysuru district has been
considered and two sampling stations were held, One at
Nanjanagudu and the other at Mahadeva Nagar and Noise
monitoring was done through noise level meters. The traffic
noise prediction for the year 2027 and 2037 is done with the
help of Federal Highway Administration (FHWA) model using
the traffic volume and speed data recorded at those two
sampling stations. The analysis of data has shown that the
observed noise levels along a highway corridorNH 150ain the
year 2027 and 2037 are alarmingly high.
Key Words: FHWA Model, Noise modeling, Traffic noise
prediction, NH-150 a, Nanjanagudu, Mahadeva Nagar
and noise monitoring.
1. INTRODUCTION
Roadway noise is the collective sound energy originating
from motor vehicles. It consists mainly of road surface, tire,
engine/transmission, aerodynamic, and decelerating
elements. Tire pavement noise is found to be the major
contributor of highway noise. Traffic operations noise is
affected expressively by vehicle speeds, since sound energy
unevenly doubles for each increment of ten miles an hour in
vehicle velocity; an exception to this rule occurs at very low
speeds where decelerating and acceleration noise dominate
over aerodynamic noise. Many cities have faced problemsof
increasing use of motor vehicles. High use of motor vehicles
has increased environmental problems such as air pollution
and traffic noise. Continuous exposuretounacceptablenoise
levels may lead to the environmental problems which might
affect quality of life of the residentssuchasdepression,sleep
disturbance, annoyance, poor working efficiency and
adverse health effects. Road traffic noise is one of the main
environmental problem that has been experienced by
residents in many cities in the world. Thegrowthproportion
of motor vehicles is at the rate of 10 percent per year. This
high increase in motor vehicles ownership has increased
environmental problems such as air pollution and noise
level. The contribution of highway noise is 70%, airway
contributes 20% and railway contributes about 10% to
overall traffic noise. There is mixed traffic on most of the
Indian highways with a wide variation in traffic volume,
speed and other road and traffic related parameters. Traffic
noise prediction is done with the help of Federal Highway
Administration Model (FHWA Model) using traffic volume
and speed recorded at several samplings stations and the
FHWA model is found to be applicable for the prediction of
traffic noise in India with some degree of accuracy. The
enormous progress in the Road Transportation Division in
India has been a key element in the economic development
In India; the national highways are the primary long-
distance roadways. They are upheld by the Central
Government, and the majority is two-lane. India has a large
road network of over 3.314 million kilometers of roadways
(2.1 million miles), which makes it a country with the third
largest road network in the world.
2. FHWA Model
Federal Highway Administration (FHWA) was used to
develop Ldncontoursforallhighwaysandmajorroadwaysin
all over the world. The FHWA Model is the analytical method
presently preferred for traffic noise prediction by most state
and local agencies.
To assess the noise levelsatthevarioussensitivereceptor
locations along the corridor, thepredictionofnoiselevelshas
been made for the horizon years 2027, 2037 using FHWA
Transport Noise Model. The Highway NoiseModelpresented
below is based upon calculating the hourly Leq for category-
wise vehicles separately and then adding these
logarithmically to obtain the overall hourly Leq value. The
FHWA TNM is a new state-of-the art computerized model
used for predicting noise impacts in the locality of highways.
It uses advance in acoustics and computer technology to
improve the accuracy and ease of modeling highway traffic
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2097
noise, including the design of efficient,cost-effectivehighway
noise barriers.
2.1 Modeling Components of FHWA
1. Five standard vehicle types, as well as user defined
vehicles.
2. Constant-flow and interrupted-flow traffic.
3. Effects of different pavement types and graded
roadways.
4. Sound-level computations based on a one-third octave-
band database and one-third octave-band
algorithms.
5. Graphically interactive noise barrier design
optimization.
6. Attenuation over/through rows of buildings and dense
vegetation.
7. Multiple diffraction analyses.
8. Contour analyses.
9. Parallel barrier analyses.
2.2 Data’s needed for modeling
1. First thing is to collect the traffic volume details of the
study area by conducting traffic surveys
2. Proper road alignment should be known such as width of
the road, type of road, Number of lanes etc.
3. Some meteorological details like temperature & humidity
should be collected.
4. During Noise monitoring, the distance of the monitoring
station should be calculated from the project road.
5. During Noise monitoring the number of dwelling units at
the monitoring station should be Known.
6. AutoCAD drawing of road alignment for project road
should be drawnand it should be converted into DXF format.
So, that it would be helpful to import the drawing into the
software for locating various things like noise monitoring
stations, barriers, buildings, terrain lines etc.
7. The traffic data collected should be forecasted for the
respective study years.
2.3 Procedure to use TNM 2.5 Software
1. First thing is to import the alignment drawing from
AutoCAD in DXF format.
2. If there is no AutoCAD file for alignment of road,proper
coordinates can be put so as to generate the alignment of
road.
3. In the main screen of the software there isamenubarit
includes File, edit, view, setup, input, calculate, barrier
analysis, tables etc. In the main screen, we can also see Tool
bar. The Tool Bar provides quick access to editing and zoom
features, as well as input objects.
4. So the data what we have collected should be
incorporated into the input bar, the input bar contains
Roadways, receivers, barriers, building rows, terrain lines,
contour zones.
5. In the roadway option, coordinates of road alignment
should be put. In the same option, we have traffic tab, traffic
volume details and the speedof the respective given vehicles
should be inputted.
6. In the input bar immediately after Roadway there is
Receiver option. The coordinatesoftheReceiverpointsofthe
study area should be incorporated.
7. After Receiver option thereis a barrier design,Building
rows, Terrain lines. Similarly, the collected data have to be
inputted into the respective options too.
8. Periodic input checks are desirable, because they catch
potential input misunderstandings before we progress
through all our input. So, there is option called as inputcheck
in the input bar.
9. TNM computations are complex and time-consuming,
select Calculate after all input items have been entered and
verified. When Calculate is selected, TNM automatically
performs a final Input Check. TNM then calculates predicted
noise levels at all receivers through a series of modifications
to a reference sound level. These modifications account for
the following sound propagation factors: divergence;
atmospheric absorption; ground characteristics and
topography; barriers; rows of buildings; and
areas of heavy vegetation. The reference sound level is
based upon vehicle noise emission levels contained within
the TNM Data Base.
10.The results of the obtained noise levels will be in the
tables menu.
3. Study area
The road NH-150A (Jewargi–Chamarajnagar Road) starts
from Jewargi, Km 0.000 and ends at Chamarajnagar, Km
638.620 (New Chainage Km 684.224)inKarnatakastate.The
total length of NH-150A has been revised and corrected
recently, hence the end chainage has been changed from Km
638.620 to 684.224. Accordingly, new chainage will be
incorporated in parenthesis for all the submission hereafter.
National Highway 150A connects Jewargi with
Chamarajnagar via Siruguppa, Bellary, Hiriyur,
Chikkanayakanahalli, Nagamangala, Srirangapatna, Mysore,
Nanjanagudu in the Stateof Karnataka. Itcatersmainlytothe
intrastate traffic apart from serving as linkage road for the
traffic destined/ originating between Jewargi &
Chamarajnagar.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2098
Fig. 1. Project Road Nanjanagudu to ChamarajnagNH150-A
The project road from Nanjanagudu to Chamarajanagar, is a
part of NH-150A, lies in the Southernmost part of Karnataka
and provides vital intrastate connectivity between Southern
districts and northern districts in Karnataka. Nanjanaguduis
famous for Srikanteshwara Temple and is also called as
"Dakshina Kashi". Project road (NH-150A) starts at Km
603.600 (New Chainage Km 646.324) the intersectionofNH-
212 and Railway level crossing near Sujathapuram and ends
at Km 616.100 (New Chainage Km 658.824) near Badnavalu
village. The length of the project road is 12.500 Kms. Project
road mainly caterstotrafficarrivingfromNationalHighway–
212 (from Mysore and nearby villages) to Srikanteshwara
Temple at Nanjangud, Chamarajanagar and other villages
apart from catering to the commuting needs of local traffic.
Traffic on the project road comprises both passenger and
freight vehicles. The existing road network and road
condition is inadequate. It is deficient to cater to the normal
traffic and the traffic likely to be generated/ attracted after
improvement. Improvements to the existingroadwillensure
enhanced driving comfort, level of service and safety. The
total length of project road section is 12.500 km.
The project road section starts from Km 603.600 (at the
intersection of NH-212 at Nanjanagudu) and ends at Km
616.100 near Badanavalu(NanjanaguduTaluk-MysuruDist.
border)
(New Chainage from Km 646.324 to Km 658.824). Along this
corridor two samplings stations were located, one at
Nanjanagudu and the other at Mahadeva nagar.
4. Indian noise standards
In India, ambient air quality standards in respect of noise
level have been prescribed under Environmental Protection
Act, 1986, which are also given in noise prevention and
control rules 2000 and the standards of noise in residential
commercial, industrialandsilenceareasindayandnighttime
are given in Table 1
Table 1. Noise standards
Area code Category of area Limits in dB(A), Leq
Day time Night time
A Industrial area 75 70
B Commercial zone 65 55
C Residential zone 55 45
D Silence zone 50 40
Day time- 6.00 AM to10.00 PM (16 hours), Night time- 10.00
PM to 6.00 AM (08 hours),
Areas up to 100 meters around certain premises like
hospitals, educational institutions and courts may be
declared as silence zone
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2099
5. Methodology
The methodology adopted is measurement of ambient noise
levels at both the sampling stations, Collections of traffic
volume and speed of the vehicles at the sampling stations.
5.1 Measurement of ambient noise levels
The Noise level monitoring was carried out at two locations
one near Hotel Mahadeshwara Palace near Shrikanteshwara
Temple at Nanjanagudu and the other one near Mahadeva
Nagar along the project corridor. Hand held noise level
meters were used to monitor the noise. Noise level in dB (A)
are collected for 24 hrs duration at both the stations.
5.2 Traffic volume
Traffic volume is premeditated manually at the selected
observation sites. Total number of vehicles passes in each
type, passing in one hour in a single direction is noted in
terms of vehicles/hour.
5.3 Speed measurement
Physical method of spot speed measurement is done for the
current study. For this purpose, two points are marked with
a known distance (100 meters) on the road at the sampling
site. With the help of a stop watch the time taken by the
vehicle to cross that distance is recorded. Dividing the
distance with the time taken in crossing the distance, the
speed is Km/h for each type of vehicle is calculated and
recorded for each hour of study.
6. Results and discussion
The ambient noise levels recorded using noiselevel meterat
the present project corridor NH 150 a has given the
following results.
Table 2. Noise level monitoring results
The noise monitoring survey shows that noise levels are
closer to the upper limit of the noise standards. This may be
due to mix activities as well as vehicular movement on the
road. Noise, though is a major area of concern, at locationsof
sensitive receptors (educational establishmentslikeschools
and colleges, etc.) identified quite close to the road.
The hourly recorded noise level at various locations in the
study area shows fluctuations because of change in traffic
movement, construction activities and other man-made
sources. The equivalent values of noise levels are 63.31 &
59.75 Which are within the prescribed norms of CPCB.
7. FHWA model results:
TABLE 3. Predicted noise level results
The above table shows the resultsofpredictednoiselevelsof
present project corridor. It is observed that the noise levels
in the year 2027 & 2037 at Nanjanagudu stationarefoundto
be 70.6 dB & 71.2 dB respectively. Similarly, for Mahadeva
nagar station Noise level is found to be 70.8 dB & 71.4 dB
respectively. The predicted noise levels can be reduced by
using suitable noise barriers.
It is seen in the table that with the usage of noise barriers
around 15 m from the roadways noise levels can be reduced
suitably. The results obtained with noise barriersintheyear
2027 & 2037 at Nanjanagudu station are found to be65.4 dB
& 66 dB respectively. Similarly, for Mahadeva nagar station
noise level is found to be 64.4 dB & 64.9 dB.
8. CONCLUSIONS
Due to huge number of high-speed vehicles plying on roads,
increased traffic volume and congestion near cities and
urban dwellings, a sharp increase around 7 to 12 dB in noise
levels has been rendered. The analysis of data has shown
that the observed noise levels along a highway corridor are
alarmingly high and the steps need to be taken for the
control of noise by the prescribed authority. It is seen that
with usage of barriers around 15m from the roadways noise
level can be reduced suitably. It is obvious that the
regulation of traffic volumeandspeedatanyplacemaybring
desired results with a view to control or minimize noise
levels along a highway corridor.
It is expected that FHWA model can be used as a successful
tool for predicting the noise using traffic parameters. With a
view to control the traffic noise, the restrictions on traffic
flow and speed can be planned especially along the highway
corridors located in the vicinity of cities and urban areas,
using the outcome of this study. It is also felt that the
regulation of traffic volume and speed at sensitive points
Location Existing
Noise
levels
Leq in dB
Predicted in
the year
(dB)
With Barriers
in the year
(dB)
2027 2037 2027 2037
Nanjanagudu 63.31 70.6 71.2 65.4 66
Mahadeva
Nagar
59.75 70.8 71.4 64.4 64.9
Location
Time
Frequenc
y
Parameters Standard
s as per
CPCB
Maximu
m
Minimu
m
Leq
dB
(A)
Nanjanagud
u
10.05AM -
10.05 AM
86.90 46.70 63.3
1
75.00
dB(A)
Mahadev
Nagar
11.25AM –
11.25 AM
80.30 46.20 59.7
5
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2100
may prove to be quite helpful in reducing the noise levels
along the highway corridors in urban areas. It is expected
that the noise control along the highways by regulation of
traffic volume and vehicle speed can be effectively
implemented in India and elsewhere and FHWA model may
prove to be of immense help in this perspective.
ACKNOWLEDGEMENT
This study was funded by the C V Kand Consultants Pvt. Ltd,
Bengaluru. The authors wishtogratefullyacknowledge Sunil
Kand (Director of C V Kand Consultants Pvt. Ltd, Bengaluru)
for giving a chance to work with the company.
REFERENCES
[1] Zannin, P. H., Ferreira, C. A. M. & Szermetta, B. (2006).
Evaluation of noise pollution in urban
parks. Environmental Monitoring and Assessment,118,
423–433.
[2] Agrawal, S. and Swami, B.L. (2011). ―Comprehensive
approach for the development of traffic noiseprediction
model for Jaipur city‖. Environ Monit Assess, 172:113-
120.
[3] Rao, R. P. & Rao, S. M. G. (1991b). Prediction of
LA10T traffic noise levels in the city of Visakhapatnam,
India. Applied Acoustics, 34, 101–110.
[4] Alberola J, Flindell H, Bullmore J. (2005), ―Variabilityin
road traffic noise levels‖, Elsevier Applied Acoustics 66
(2005) 1180–1195.
[5] Piccolo, A., Plutino, D. & Cannistraaro, G. (2004).
Evaluation and analysis of the environmental noise of
Messina, Italy. Applied Acoustics, 65, 343–364.
[6] Phatak, V., Tripathi, B. D. & Mishra, V. K. (2008b).
Evaluation of traffic noise prediction and attitudes of
exposed individuals in working place. Atmospheric
Environment, 42, 3892–3898.
[7] Michaud, D. S., Keith, S. E. & Mcmurchy, D. (2008). Noise
annoyance in Canada. Noise and Health, 7(27), 39–47.
[8] E. Chevallier, A. Can, M. Nadji, L. Leclercq, ―Improving
noise assessment at intersections by modeling traffic
dynamics‖, Transportation Research Part D 14 (2009)
100–110
[9] Steele, C. 2001. ―A critical review of some traffic noise
prediction models‖, Applied Acoustics 62, pp. 271-287.
[10] IRC: 104-1988. (1989). ―Guidelines for
Environmental Impact AssessmentofHighwayProject‖.
The Indian Roads Congress,JamnagarHouse,NewDelhi.
[11] IS: 10399-1982. (1983). ―Methods for
Measurement of Noise Emitted by Stationary Road
Vehicles‖. Bureau of Indian Standards. New Delhi.

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Prediction of Noise Levels using FHWA Model for National highway 150 A (NH 150-A)

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2096 Prediction of noise levels using FHWA Model for National highway 150 A (NH 150-A) Sagar Pashupatihal, Sneha R, Sumanth K 1(Dept. of Environmental Engineering, Manipal Institute of Technology, Manipal, India) 2(Dept. of Civil Engineering, Manipal Institute of Technology, Manipal, India) 3(Senior highway Engineer, C V Kand Consultants Pvt. Ltd, Bengaluru, India) ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract - Population growth and developmentofactivities in cities have a great influence on the development of transportation sector. The high growthrateofprivatevehicles is mainly due to increase in the population. This condition has enlarged environmental degradation, not only in terms offuel consumption but also in terms of air pollutionandtrafficnoise generated by vehicles. Noise generated by traffic is having many adverse effects such as increase of stress, sleep disturbance, communication difficulty and also hearing problem. In order to overcome these problems, itisrequiredto estimate the level of traffic noise produced by traffic volume and average speed of the vehicles. In the present work, the traffic noise along a highway corridor on NH-150A passing through Nanjanagudu city of Mysuru district has been considered and two sampling stations were held, One at Nanjanagudu and the other at Mahadeva Nagar and Noise monitoring was done through noise level meters. The traffic noise prediction for the year 2027 and 2037 is done with the help of Federal Highway Administration (FHWA) model using the traffic volume and speed data recorded at those two sampling stations. The analysis of data has shown that the observed noise levels along a highway corridorNH 150ain the year 2027 and 2037 are alarmingly high. Key Words: FHWA Model, Noise modeling, Traffic noise prediction, NH-150 a, Nanjanagudu, Mahadeva Nagar and noise monitoring. 1. INTRODUCTION Roadway noise is the collective sound energy originating from motor vehicles. It consists mainly of road surface, tire, engine/transmission, aerodynamic, and decelerating elements. Tire pavement noise is found to be the major contributor of highway noise. Traffic operations noise is affected expressively by vehicle speeds, since sound energy unevenly doubles for each increment of ten miles an hour in vehicle velocity; an exception to this rule occurs at very low speeds where decelerating and acceleration noise dominate over aerodynamic noise. Many cities have faced problemsof increasing use of motor vehicles. High use of motor vehicles has increased environmental problems such as air pollution and traffic noise. Continuous exposuretounacceptablenoise levels may lead to the environmental problems which might affect quality of life of the residentssuchasdepression,sleep disturbance, annoyance, poor working efficiency and adverse health effects. Road traffic noise is one of the main environmental problem that has been experienced by residents in many cities in the world. Thegrowthproportion of motor vehicles is at the rate of 10 percent per year. This high increase in motor vehicles ownership has increased environmental problems such as air pollution and noise level. The contribution of highway noise is 70%, airway contributes 20% and railway contributes about 10% to overall traffic noise. There is mixed traffic on most of the Indian highways with a wide variation in traffic volume, speed and other road and traffic related parameters. Traffic noise prediction is done with the help of Federal Highway Administration Model (FHWA Model) using traffic volume and speed recorded at several samplings stations and the FHWA model is found to be applicable for the prediction of traffic noise in India with some degree of accuracy. The enormous progress in the Road Transportation Division in India has been a key element in the economic development In India; the national highways are the primary long- distance roadways. They are upheld by the Central Government, and the majority is two-lane. India has a large road network of over 3.314 million kilometers of roadways (2.1 million miles), which makes it a country with the third largest road network in the world. 2. FHWA Model Federal Highway Administration (FHWA) was used to develop Ldncontoursforallhighwaysandmajorroadwaysin all over the world. The FHWA Model is the analytical method presently preferred for traffic noise prediction by most state and local agencies. To assess the noise levelsatthevarioussensitivereceptor locations along the corridor, thepredictionofnoiselevelshas been made for the horizon years 2027, 2037 using FHWA Transport Noise Model. The Highway NoiseModelpresented below is based upon calculating the hourly Leq for category- wise vehicles separately and then adding these logarithmically to obtain the overall hourly Leq value. The FHWA TNM is a new state-of-the art computerized model used for predicting noise impacts in the locality of highways. It uses advance in acoustics and computer technology to improve the accuracy and ease of modeling highway traffic
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2097 noise, including the design of efficient,cost-effectivehighway noise barriers. 2.1 Modeling Components of FHWA 1. Five standard vehicle types, as well as user defined vehicles. 2. Constant-flow and interrupted-flow traffic. 3. Effects of different pavement types and graded roadways. 4. Sound-level computations based on a one-third octave- band database and one-third octave-band algorithms. 5. Graphically interactive noise barrier design optimization. 6. Attenuation over/through rows of buildings and dense vegetation. 7. Multiple diffraction analyses. 8. Contour analyses. 9. Parallel barrier analyses. 2.2 Data’s needed for modeling 1. First thing is to collect the traffic volume details of the study area by conducting traffic surveys 2. Proper road alignment should be known such as width of the road, type of road, Number of lanes etc. 3. Some meteorological details like temperature & humidity should be collected. 4. During Noise monitoring, the distance of the monitoring station should be calculated from the project road. 5. During Noise monitoring the number of dwelling units at the monitoring station should be Known. 6. AutoCAD drawing of road alignment for project road should be drawnand it should be converted into DXF format. So, that it would be helpful to import the drawing into the software for locating various things like noise monitoring stations, barriers, buildings, terrain lines etc. 7. The traffic data collected should be forecasted for the respective study years. 2.3 Procedure to use TNM 2.5 Software 1. First thing is to import the alignment drawing from AutoCAD in DXF format. 2. If there is no AutoCAD file for alignment of road,proper coordinates can be put so as to generate the alignment of road. 3. In the main screen of the software there isamenubarit includes File, edit, view, setup, input, calculate, barrier analysis, tables etc. In the main screen, we can also see Tool bar. The Tool Bar provides quick access to editing and zoom features, as well as input objects. 4. So the data what we have collected should be incorporated into the input bar, the input bar contains Roadways, receivers, barriers, building rows, terrain lines, contour zones. 5. In the roadway option, coordinates of road alignment should be put. In the same option, we have traffic tab, traffic volume details and the speedof the respective given vehicles should be inputted. 6. In the input bar immediately after Roadway there is Receiver option. The coordinatesoftheReceiverpointsofthe study area should be incorporated. 7. After Receiver option thereis a barrier design,Building rows, Terrain lines. Similarly, the collected data have to be inputted into the respective options too. 8. Periodic input checks are desirable, because they catch potential input misunderstandings before we progress through all our input. So, there is option called as inputcheck in the input bar. 9. TNM computations are complex and time-consuming, select Calculate after all input items have been entered and verified. When Calculate is selected, TNM automatically performs a final Input Check. TNM then calculates predicted noise levels at all receivers through a series of modifications to a reference sound level. These modifications account for the following sound propagation factors: divergence; atmospheric absorption; ground characteristics and topography; barriers; rows of buildings; and areas of heavy vegetation. The reference sound level is based upon vehicle noise emission levels contained within the TNM Data Base. 10.The results of the obtained noise levels will be in the tables menu. 3. Study area The road NH-150A (Jewargi–Chamarajnagar Road) starts from Jewargi, Km 0.000 and ends at Chamarajnagar, Km 638.620 (New Chainage Km 684.224)inKarnatakastate.The total length of NH-150A has been revised and corrected recently, hence the end chainage has been changed from Km 638.620 to 684.224. Accordingly, new chainage will be incorporated in parenthesis for all the submission hereafter. National Highway 150A connects Jewargi with Chamarajnagar via Siruguppa, Bellary, Hiriyur, Chikkanayakanahalli, Nagamangala, Srirangapatna, Mysore, Nanjanagudu in the Stateof Karnataka. Itcatersmainlytothe intrastate traffic apart from serving as linkage road for the traffic destined/ originating between Jewargi & Chamarajnagar.
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2098 Fig. 1. Project Road Nanjanagudu to ChamarajnagNH150-A The project road from Nanjanagudu to Chamarajanagar, is a part of NH-150A, lies in the Southernmost part of Karnataka and provides vital intrastate connectivity between Southern districts and northern districts in Karnataka. Nanjanaguduis famous for Srikanteshwara Temple and is also called as "Dakshina Kashi". Project road (NH-150A) starts at Km 603.600 (New Chainage Km 646.324) the intersectionofNH- 212 and Railway level crossing near Sujathapuram and ends at Km 616.100 (New Chainage Km 658.824) near Badnavalu village. The length of the project road is 12.500 Kms. Project road mainly caterstotrafficarrivingfromNationalHighway– 212 (from Mysore and nearby villages) to Srikanteshwara Temple at Nanjangud, Chamarajanagar and other villages apart from catering to the commuting needs of local traffic. Traffic on the project road comprises both passenger and freight vehicles. The existing road network and road condition is inadequate. It is deficient to cater to the normal traffic and the traffic likely to be generated/ attracted after improvement. Improvements to the existingroadwillensure enhanced driving comfort, level of service and safety. The total length of project road section is 12.500 km. The project road section starts from Km 603.600 (at the intersection of NH-212 at Nanjanagudu) and ends at Km 616.100 near Badanavalu(NanjanaguduTaluk-MysuruDist. border) (New Chainage from Km 646.324 to Km 658.824). Along this corridor two samplings stations were located, one at Nanjanagudu and the other at Mahadeva nagar. 4. Indian noise standards In India, ambient air quality standards in respect of noise level have been prescribed under Environmental Protection Act, 1986, which are also given in noise prevention and control rules 2000 and the standards of noise in residential commercial, industrialandsilenceareasindayandnighttime are given in Table 1 Table 1. Noise standards Area code Category of area Limits in dB(A), Leq Day time Night time A Industrial area 75 70 B Commercial zone 65 55 C Residential zone 55 45 D Silence zone 50 40 Day time- 6.00 AM to10.00 PM (16 hours), Night time- 10.00 PM to 6.00 AM (08 hours), Areas up to 100 meters around certain premises like hospitals, educational institutions and courts may be declared as silence zone
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2099 5. Methodology The methodology adopted is measurement of ambient noise levels at both the sampling stations, Collections of traffic volume and speed of the vehicles at the sampling stations. 5.1 Measurement of ambient noise levels The Noise level monitoring was carried out at two locations one near Hotel Mahadeshwara Palace near Shrikanteshwara Temple at Nanjanagudu and the other one near Mahadeva Nagar along the project corridor. Hand held noise level meters were used to monitor the noise. Noise level in dB (A) are collected for 24 hrs duration at both the stations. 5.2 Traffic volume Traffic volume is premeditated manually at the selected observation sites. Total number of vehicles passes in each type, passing in one hour in a single direction is noted in terms of vehicles/hour. 5.3 Speed measurement Physical method of spot speed measurement is done for the current study. For this purpose, two points are marked with a known distance (100 meters) on the road at the sampling site. With the help of a stop watch the time taken by the vehicle to cross that distance is recorded. Dividing the distance with the time taken in crossing the distance, the speed is Km/h for each type of vehicle is calculated and recorded for each hour of study. 6. Results and discussion The ambient noise levels recorded using noiselevel meterat the present project corridor NH 150 a has given the following results. Table 2. Noise level monitoring results The noise monitoring survey shows that noise levels are closer to the upper limit of the noise standards. This may be due to mix activities as well as vehicular movement on the road. Noise, though is a major area of concern, at locationsof sensitive receptors (educational establishmentslikeschools and colleges, etc.) identified quite close to the road. The hourly recorded noise level at various locations in the study area shows fluctuations because of change in traffic movement, construction activities and other man-made sources. The equivalent values of noise levels are 63.31 & 59.75 Which are within the prescribed norms of CPCB. 7. FHWA model results: TABLE 3. Predicted noise level results The above table shows the resultsofpredictednoiselevelsof present project corridor. It is observed that the noise levels in the year 2027 & 2037 at Nanjanagudu stationarefoundto be 70.6 dB & 71.2 dB respectively. Similarly, for Mahadeva nagar station Noise level is found to be 70.8 dB & 71.4 dB respectively. The predicted noise levels can be reduced by using suitable noise barriers. It is seen in the table that with the usage of noise barriers around 15 m from the roadways noise levels can be reduced suitably. The results obtained with noise barriersintheyear 2027 & 2037 at Nanjanagudu station are found to be65.4 dB & 66 dB respectively. Similarly, for Mahadeva nagar station noise level is found to be 64.4 dB & 64.9 dB. 8. CONCLUSIONS Due to huge number of high-speed vehicles plying on roads, increased traffic volume and congestion near cities and urban dwellings, a sharp increase around 7 to 12 dB in noise levels has been rendered. The analysis of data has shown that the observed noise levels along a highway corridor are alarmingly high and the steps need to be taken for the control of noise by the prescribed authority. It is seen that with usage of barriers around 15m from the roadways noise level can be reduced suitably. It is obvious that the regulation of traffic volumeandspeedatanyplacemaybring desired results with a view to control or minimize noise levels along a highway corridor. It is expected that FHWA model can be used as a successful tool for predicting the noise using traffic parameters. With a view to control the traffic noise, the restrictions on traffic flow and speed can be planned especially along the highway corridors located in the vicinity of cities and urban areas, using the outcome of this study. It is also felt that the regulation of traffic volume and speed at sensitive points Location Existing Noise levels Leq in dB Predicted in the year (dB) With Barriers in the year (dB) 2027 2037 2027 2037 Nanjanagudu 63.31 70.6 71.2 65.4 66 Mahadeva Nagar 59.75 70.8 71.4 64.4 64.9 Location Time Frequenc y Parameters Standard s as per CPCB Maximu m Minimu m Leq dB (A) Nanjanagud u 10.05AM - 10.05 AM 86.90 46.70 63.3 1 75.00 dB(A) Mahadev Nagar 11.25AM – 11.25 AM 80.30 46.20 59.7 5
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 2100 may prove to be quite helpful in reducing the noise levels along the highway corridors in urban areas. It is expected that the noise control along the highways by regulation of traffic volume and vehicle speed can be effectively implemented in India and elsewhere and FHWA model may prove to be of immense help in this perspective. ACKNOWLEDGEMENT This study was funded by the C V Kand Consultants Pvt. Ltd, Bengaluru. The authors wishtogratefullyacknowledge Sunil Kand (Director of C V Kand Consultants Pvt. Ltd, Bengaluru) for giving a chance to work with the company. REFERENCES [1] Zannin, P. H., Ferreira, C. A. M. & Szermetta, B. (2006). Evaluation of noise pollution in urban parks. Environmental Monitoring and Assessment,118, 423–433. [2] Agrawal, S. and Swami, B.L. (2011). ―Comprehensive approach for the development of traffic noiseprediction model for Jaipur city‖. Environ Monit Assess, 172:113- 120. [3] Rao, R. P. & Rao, S. M. G. (1991b). Prediction of LA10T traffic noise levels in the city of Visakhapatnam, India. Applied Acoustics, 34, 101–110. [4] Alberola J, Flindell H, Bullmore J. (2005), ―Variabilityin road traffic noise levels‖, Elsevier Applied Acoustics 66 (2005) 1180–1195. [5] Piccolo, A., Plutino, D. & Cannistraaro, G. (2004). Evaluation and analysis of the environmental noise of Messina, Italy. Applied Acoustics, 65, 343–364. [6] Phatak, V., Tripathi, B. D. & Mishra, V. K. (2008b). Evaluation of traffic noise prediction and attitudes of exposed individuals in working place. Atmospheric Environment, 42, 3892–3898. [7] Michaud, D. S., Keith, S. E. & Mcmurchy, D. (2008). Noise annoyance in Canada. Noise and Health, 7(27), 39–47. [8] E. Chevallier, A. Can, M. Nadji, L. Leclercq, ―Improving noise assessment at intersections by modeling traffic dynamics‖, Transportation Research Part D 14 (2009) 100–110 [9] Steele, C. 2001. ―A critical review of some traffic noise prediction models‖, Applied Acoustics 62, pp. 271-287. [10] IRC: 104-1988. (1989). ―Guidelines for Environmental Impact AssessmentofHighwayProject‖. The Indian Roads Congress,JamnagarHouse,NewDelhi. [11] IS: 10399-1982. (1983). ―Methods for Measurement of Noise Emitted by Stationary Road Vehicles‖. Bureau of Indian Standards. New Delhi.