Air |
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SOLID WASTE |
AGRICULTURE |
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CLIMATE |
DEMOGRAPHY |
BIODIVERSITY |
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Save Ganga Save Dolphin |
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NOISE POLUTION
Background |
Frequencies Ranges for Hearing and Speaking by Human and Animals |
Loudness, Intensity, and dB |
Sound Level in dB of Some Common Sound |
Sound Pressure, Sound Pressure Level, Sound Power and Sound Power Level |
How Do We Hear |
Sound and Noise |
Type of Noise |
Ambient Noise |
Noise and Its Impact |
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Noise Pollution |
Air Act & Noise Rules |
Noise Status |
Noise Level Std. |
Protecting the Commons |
Noise level on Diwali-2011 |
Action Plan |
Monitoring Network |
We Can Help |
Background
Sound is a form of energy. It is that external physical cause which produces the sensation of hearing in our ears. Sound is produced only when some material body is made to vibrate. It requires material medium for its propagation and cannot travel in vacuum because there are no material particles which can vibrate and propagate energy. The vibrations travel through the medium in form of waves with a certain speed depending on the density and elasticity of the medium. When vibrations reach our ear, sound is heard. Our ears are sensitive only to a limited range of frequencies 20 Hz to 20,000 Hz. This range of frequency is, therefore, called the audible range of sound. The sound of frequency above 20,000 Hz is called the ultrasonic, while the sound of frequency below 20 Hz is called the infrasonic. Ultrasonic and infrasonic both are inaudible to human beings. Ultra sound used in medical diagnosis. Infra sound produced in earthquakes.
Different animals have different ranges of audible frequencies. A dog can hear sounds of frequencies up to nearly 50 kHz, a bat up to about 100 kHz, while Dolphins can hear sounds of even higher frequencies up to 150 kHz. The animals can also produce ultrasonic sounds and can communicate in them. Elephants and Whales produce sounds of frequencies less than 20 Hz. Some fishes can hear sounds of frequencies in the range of 1 Hz to 25 Hz.
Frequency Ranges for Hearing and Speaking by Human and Animals
Object |
Frequency Range of Hearing and Speaking |
Bat |
10 Hz – 100kHz |
Cat |
80 Hz – 60 kHz |
Dog |
20 Hz – 50 kHz |
Dolphins |
200 Hz – 150 kHz |
Grasshopper |
90 Hz – 1.0 kHz |
Human |
20 Hz – 20kHz |
Loudness, Intensity and dB
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Loudness is the property by virtue of which a loud sound can be distinguished from a faint one, both having the same quality. Loudness is an aural sensation, i.e., a physiological rather than a physical phenomenon; |
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The louder a sound is, the more energy its sound waves carry. Loudness is measured in decibels(dB).Sound of 0 dB are just audible to the human ear, while sound of 130 dB or more cause pain; |
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Loudness of sound depends on intensity of the wave, however, loudness is not the same as intensity. Intensity is a measurable quantity, while loudness is a sensation; |
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Experimentally, Weber and Fechner established a relationship between the loudness L and intensity I which is given as: L = K log10I, where K is a constant of proportionality. Thus, loudness is proportional to the logarithmic value of the intensity, but not in the same proportion. Relation between the two is not linear. |
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The intensity at any point of the medium is measured as the amount of sound energy passing per second normally through unit area at that point. Its unit is microwatt per metre² (which is equal to 10-6 joule per second per metre²). |
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The intensity of normal sound is nearly 10µW m-2 while minimum intensity of sound audible to ears is 10-6µW m-2. Greater the energy carried by a sound wave, greater is the intensity of sound, hence louder it seems to us. The intensity of a sound wave in air is proportional to (i)the square of the amplitude of vibration,(ii)the square of the frequency of vibration and(iii)the density of air. |
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The sound level is usually expressed in decibel(dB).If at a given frequency, I1 and I0 are intensities of two sounds, which loudness are L1 and L0 then difference in loudness of the two sounds L is:
L = L1 - L0 = K(log10I1 – log10I0) or L = K log10 |
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If, I0 is taken as reference intensity (10-12µW m-2), the minimum intensity of audible sound intensity at frequency 1 kHz, then L is called the sound level.
Taking K = 1, the sound level is L = log10 |
( |
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) |
ForI1 = I0, sound level L = 0 dB, sound of intensity 10-12µW m-2 at 1 kHz has loudness zero dB.
For an increase in intensity at a point by 100 times the initial value, the increase in sound level will be 10 log10 100 = 20 dB. For an increase in intensity at a point by 100,00 times the initial value, the increase in sound level will be 10 log10 100,00 = 40 dB. It means that for 100 times increase in intensity, the loudness get doubled.
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the inventor of telephone. |
the scientist Alexander Graham Bel,
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1 dB is defined as the change in level of loudness when the intensity of sound changes by 26%. |
Sound Pressure, Sound Pressure Level Sound Power, Sound Power Level
Intensity is the energy/time/area; and since the energy/time ratio is equivalent to the quantity “power” , hence, intensity is simply the power/area.
Therefore, sound strength is measured as sound pressure, sound pressure level or sound power, sound power level (in decibels).
Sound Pressure
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The Sound Pressure is the force (N) of sound on a surface area (m2) perpendicular to the direction of the sound. The SI-unit for the Sound Pressure is N/m2 or Pa. |
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Sound is usually measured with microphones responding proportionally to the sound pressure - p. The power in a sound wave goes as the square of the pressure. |
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The lowest sound pressure possible to hear is approximately 2 10-5 Pa (20 micro Pascal, 0.02 mPa), 2 ten billionths of an atmosphere. |
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It is therefore, convenient to express the sound pressure as a logarithmic decibel scale related to this lowest human hearable sound - 2 10-5 Pa, 0 dB. |
Sound Pressure Level
Where,
Lp = sound pressure level (dB)
p = sound pressure (Pa)
pref = 2 10-5 - reference sound pressure (Pa)
If the pressure is doubled, the sound pressure level is increased with 6 dB (20 log (2)).
Sound Power
Sound power is the energy rate - the energy of sound per unit of time (J/s, W in SI-unit) from a sound source.
Sound Power Level
Sound power can more practically be expressed as a relation to the threshold of hearing - 10-12 W - in a logarithmic scale named Sound Power Level - Lw, expressed as:
Lw = 10 log (N / No)
Where,
Lw = Sound Power Level in Decibel (dB)
N = sound power (W)
No = 10-12 - reference sound power (W).
Human hearable Sound Power spans from 10-12 W to 10 - 100 W, a range of 10/10-12 = 1013.
Sound Level in dB of Some Common Sound
Object Producing Sound |
Sound Level(dB) |
Jet at takeoff |
140 |
Dropping Pin(minimum audible sound) |
0 |
Normal Conversation |
50 |
Motorcycle or Car |
80 |
HOW DO WE HEAR
The Human hear consist of three main parts; the outer ear, middle ear and inner ear.
The outer ear consists of:
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The ear lobe (pinna or auricle) |
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The ear canal, through which sound waves pass to the ear drum |
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The ear drum (Tympanic membrane that separates the outer ear from the middle ear) |
The ear lobe and the outer ear canal, which delivers sound to the middle ear, make up the outer ear. Within the outer ear canal are wax- producing glands and hairs that protect the middle ear.
The ear drum is a thin, semitransparent, oval-shaped membrane that separates the middle ear from the outer ear. Its purpose is to vibrate according to the frequency and amplitude of sounds that strike it.
The Purpose of the middle ear is to:
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Transmit and amplify sounds from the eardrum to the oval window. |
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Act as a dampener on loud sounds that may damage that inner ear (cochlea). |
The middle ear acts as an impedance matching device and has three small bones operating as a set of levers. These bones transfer the vibration to the inner ear which consists of two separate systems, the semi-circular canals for controlling balance and cochlea.
The inner ear consists of:
Two chambers called the vestibular labyrinth and the cochlea.
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The vestibular labyrinth consists of elaborately formed canals (3 semicircular tubes that connect to one another), which are largely responsible for the sense of balance. |
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The cochlea, which begins at the oval window, curves into a shape that resembles a snail shell. Tiny hairs line the curves of the cochlea. Both the labyrinth and cochlea are filled with various fluids. |
The cochlea is a fluid-filled, snailed-shaped tube which is divided longitudinally into two parts by the basilar membrane. In response to an acoustic stimulus the fluid in the cochlea is disturbed and this distorts the basilar membrane on whose upper surfaces are thousands of bery sensitive hair cells. The hair cells register this distortion and transform it into nerve impulses which are transmitted to the brain. Brain is sent these messages (translated from vibrations by the cilia) through the auditory nerve. Our brain then translates all that and tells what we are hearing. Neurologists don’t yet fully understand how we process raw sound date once it enters the cerebral cortex. In the brain.
Sound and Noise
Sound is that part of energy which excites in us, the sensation of hearing. This is because some type of energy originating from the source and is entering our ear. Sound becomes unwanted when it either interferes with normal activities such as sleeping, conversation, or disrupts or diminishes one’s quality of life and such sound is known as unwanted sound, hence we call it sound pollutant or Noise. The traditional definition of noise is also “unwanted or disturbing sound”. A sound might be unwanted because it is:
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Loud |
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Unpleasant |
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Intrusive or distracting |
A constant hearing of sound of level above 120 dB can cause headache and permanent damage to the ears of the listeners. The sound of level 30 dB to 10 dB has the soothing sensation, while the level 0 dB of loudness of sound represents the limit of hearing. We should not confused about the limit of hearing with the limit of audibility. The limit audibility refers to the frequency of sound 20 Hz to 20 kHz which a man can hear, while the limit of hearing is the level of loudness (=0 dB) which a man can hear. Noise is also considered a mixture of many different sound frequencies at high decibels levels.
Type of Noise
1.
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Continuous Noise: Continuous noise is produced by machinery that operates without interruption in the same mode, for example blowers, pumps and processing equipment. Measuring for just a few minutes with hand-held equipment is sufficient to determine the noise level. |
2.
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Intermittent Noise: When machinery operates in cycles, or when single vehicles or airplanes pass by, the noise level increases and decreases rapidly. For each cycle of a machinery noise source, the noise level can be measured just as for continuous noise. A single passing vehicle or aircraft is called an event. To measure the noise of an event, the sound exposure level is measured, combining level and duration into a single description. |
3.
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Impulsive Noise: The noise from impacts or explosions, e.g. from a pile driver, punch press or gun short is called impulsive noise. It is brief and abrupt, and its startling effects cause greater annoyance than would be expected from a simple measurement of sound pressure level. |
Classification of Noise
1. |
Ambient Noise: It is the noise from all sources combined-factory noise, traffic noise, bird song etc. |
2.
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Specific Noise: specific noise is the noise from the source under investigation. The specific noise is a component of the ambient noise and can be identified and associated with specific source. Are also major sources. Additional noise pollution is contributed by office machines, sirens, power tools, and other equipment. |
3.
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Residual Noise: Residual Noise is ambient noise without specific noise. The residual noise is the noise remaining at a point under certain conditions when the noise from the specific source is suppressed. |
3. |
Background noise: Background noise is also a common one but should not
be confused with residual noise. |
Noise Pollution
Noise Pollution refers to sound in the environment that are caused by humans and that threaten the health or welfare of human or animal inhabitants.
The most common source of noise pollution by far, the one that affects the most people on the planet, is loudspeaker, siren, motor vehicles. Aircraft and industrial machinery are also sources. Additional noise pollution is contributed by office machines, sirens, power tools, and other equipment. The response of ear to sound is very dependent on the frequency content of the sound. The ear has a peak response around 2.5-3 kHz and has a relatively low response at low frequencies. Threshold of Pain: sound level at which the ear starts to feel pain. The threshold of pain is different for sound of different frequencies.
NOISE AND ITS IMPACT
7.1 Human health
Noise health effects are other health and behavioural in nature. The unwanted sound is called noise. This unwanted sound can damage physiological and psychological health. Noise pollution can cause annoyance and aggression, hypertension, high stress levels, tinnitus, hearing loss, sleep disturbances, and other harmful effects. Furthermore, stress and hypertension are the leading causes to health problems, whereas tinnitus can lead to forgetfulness, severe depression and at times panic attacks.
High noise levels can contribute to cardiovascular effects and exposure to moderately high levels during a single eight hour period causes a statistical rise in blood pressure of five to ten points and an increase in stress. Noise health effects are the health consequences of elevated sound levels. Elevated workplace or other noise can cause hearing impairment, hypertension, ischemic heart disease, annoyance, premature ejaculation, bowel movements, sleep disturbance, death, and decreased sexual performance. Changes in the immune system and birth defects have been attributed to noise exposure, but evidence is limited. Beyond these effects, elevated noise levels can create stress, increase workplace accident rates, and stimulate aggression and other anti-social behaviour. The most significant causes are vehicle and aircraft noise, prolonged exposure to loud music, and industrial noise.
Hearing Damage:
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Well established effect, caused by prolonged exposure to intense sound. |
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Impairs ability to understand speech. |
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Permanent and irreversible, even with hearing aids. |
7.2 Animal Health:
In general, a noise impact to wildlife can be determined by the degree to which the noise disrupts a functioning ecosystem. Noise has the potential to affect wildlife in a variety of ways, varying between different types of animals. Research shows that the degree of reaction to noise often varies with age, sex, season, situation, previous exposure to noise (habituation), noise level, and frequency spectrum. Potential noise effects on wildlife include; auditory damage, physiological changes and behavioural alterations. These effects are further characterized into primary and secondary effects. Primary effects are direct physical effects to the animal. Secondary effects are indirect changes which occur between the animal and its environment.
Type of Effect |
Primary |
Secondary |
Auditory |
Hearing Loss |
Change in Predator-Prey relationships |
Threshold Shift |
Mating Interference |
Physiological |
Stress |
Reduced Reproductive Capacity |
Metabolic Change |
Weakened Immune System |
Hormonal Change |
Reduction in Functioning |
Behavioral |
Signal Masking |
Change in Predator-Prey relationships |
Avoidance Behaviour |
Population Reduction |
Migration and Loss of Habitat |
Mating Interference |
Physiological Effects- Physiological effects, such as metabolic and hormonal changes, are often associated with stress. Stress in wildlife in their natural setting is typically a difficult response to quantify. For wildlife, stress reactions are part of survival and a routine occurrence. Stress reactions involve what is commonly referred to as the “fight or flight” response. When this reaction is inappropriate, such as fleeing from a non-threaten noise, impacts begin to occur. Inappropriate reactions unnecessarily to deplete an animal’s energy resources which can increase susceptibility to predators, disease, and starvation.
Behavioural Effects- Changes in normal behavioural patterns are the most apparent effects of noise on wildlife. When noise becomes an objectionable intrusion on wildlife habitat, these changes include alterations in habitat locations and migration patterns, and abnormal behaviour that can cause difficulty in mating and survival.
AIR ACT & NOISE RULES
8.1 AIR ACT & NOISE RULES
Under section 2(a) of Air (Prevention and Control of Pollution) Act, 1981 noise is defined as air pollutant
“Air pollutant” means any solid, liquid or gaseous substance [(including noise)] present in the atmosphere in such concentration as may be or tend to be injurious to human beings or other living creatures or plants or property or environment.”
Increasing ambient noise level in public places from various sources, inter-alia, industry activity, construction activity, generators sets, loud speakers, public address systems, music systems, vehicular gowns and other mechanical devices have deleterious effects on human health and the psychological well being of the people. Therefore, it is considered necessary to regulate and control of noise producing and generating sources with the objective of maintaining the ambient air quality standards in respect of noise. Central Government notified the Noise Pollution (Regulation and Control) Rules, 2000 as it is published in the Gazette of India, Extraordinary, Part-II – section 3 (ii), vide S.O 123 (E) dated 14.2.2000. In reference to above mentioned rules following responsibilities are vested with State Governments. District Magistrate, Police Commissioner, or any other officer not below the rank or Deputy Superintendent of Police:
1. |
Enforcement of Noise Pollution control measures and the due compliance of ambient air quality standards in respect of noise. |
2. |
Restriction on the use of Loud Speakers/Public Address system. |
3. |
Restriction on the use of Horns, Sound emitting construction equipment and bursting of Fire crackers. |
4. |
Prohibition of continuance Music Sound or Noise. |
5. |
Authority shall act on the complaint and take action against the violator in accordance with the provisions of rules. |
6. |
Disallowing sound producing instrument after 10 p.m to 6 a.m except in closed premises. |
7.
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State Government may permit loud speakers or public address system in night hours (between 10.00 p.m. to 12.00 midnight not exceeding 15 days in year. |
Ambient Air Quality Standards in Respect of Noise is notified under Noise Pollution (Regulation and Control) Rules, 2000.
Area Code |
Category of Area/ Zone |
Limit in dB (A) Leq* |
Day Time |
Night Time |
A |
Industrial Area |
75 |
70 |
B |
Commercial Area |
65 |
55 |
C |
Residential Area |
55 |
45 |
D |
Silence Zone |
50 |
40 |
Note:
1. |
Day time shall mean from 6 AM to 10 PM |
2. |
Night time shall mean from 10 PM to 6 AM |
3.
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Silence Zone is defined as areas up to 100 meters around such premises as hospitals, educational institutes and courts. The Silence Zones are to be declared by competent authority. |
4.
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Mixed categories of areas may be declared as one of the four above mentioned categories by the competent authority. *dB(A) Leq denotes the time weighted average of the level of sound in decibels on scale A which is relatable to human hearing. A “decibel” is a unit in which noise is measured.
“A”, in dB (A) Leq, denotes the frequency weighting in the measurement of noise and corresponds to frequency response characteristics of the human ear. Leq: It is energy mean of the noise level over a specific period.
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NOISE STATUS
Ambient Noise Level of Patna Town during year 2010-2011
Sl. No. |
Name of Sampling Location |
Ambiant Noise level in dB(A) Leq |
Remarks |
1 |
2 |
3 |
4 |
Zone Category : Sensitive zone |
Day time Standards in respect of noise 06:00 a.m to 10:00 p.m: 50 dB(A) Leq |
1. |
Hai Hospital Campus, Near Portico, Patna |
63.3 |
Road Traffic & Commercial. |
2. |
IGIMS Campus, Sheikhapura Near IGMurti |
51.1 |
Patient activities |
3. |
Patna High Court Campus, Patna |
51.4 |
Official activities |
4. |
Old Secretariat Campus, Patna (In front of Watch) |
46.2 |
--Do-- |
5. |
A. N. College Campus (In front of Technical Block) |
69.3 |
Road traffic noise |
6. |
Near main gate of Loyola High School, Kurji |
78.1 |
Traffic& communities activity |
7 |
St. Michael High School Campus |
49.5 |
Inside the campus |
8. |
Kurji Holy Family Hospital Campus |
48.2 |
Hospital activities |
9. |
Bankipur Girls School Campus, Patna |
50.0 |
School activities |
10. |
Magadha Mahila College (Campus) |
52.0 |
Campus activities |
11. |
Kachhari near D.M. office campus |
63.2 |
Public activities |
12. |
P.M.C.H. Campus, near Tata Ward |
48.3 |
Hospital& Vehicle activities |
13. |
Patna College Campus, In front of Geography Deptt |
64.2 |
College & Road Vehicle activities |
14. |
Science College Campus In front of Gymnasium |
49.4 |
Campus activities |
15. |
Law College Campus, |
52.4 |
Campus activities |
16. |
Tri-Polia Hospital campus |
61.3 |
--Do-- |
17. |
Patna City Sub Divisional office gate |
68.5 |
Traffic & Office activies |
18. |
D.A.V. Public School, BSEB Colony, Punaichak |
53.4 |
School activities |
19. |
Patna Museum, Campus, Patna. |
50.0 |
Visitor activities |
20. |
G.P.O. Campus |
52.6 |
Vehicular & Local activities |
21. |
Rajendra Nagar Hospital, Patna |
48.1 |
Hospital activities |
22. |
N.M.C.H. Campus, Patna-20 Near to main gate |
66.8 |
Traffic activities |
23. |
Bihar pharmacy college, Agamkuan, Patna |
48.2 |
Campus activities |
Zone Category: Residential Zone |
Day time Standards in respect of noise 06:00 a.m. to 10:00 p.m: 55 dB(A) Leq |
24. |
Ashiana Nagar Colony near SBI |
52.6 |
Local activities |
25. |
Magistrate colony, Ashiyana Nagar, N. Community Hall. |
48.4 |
--Do-- |
26. |
Ashiyana, near Ramnagari more |
57.8 |
Communities activities |
27. |
A.G. Colony, Near Park, Patna-25 |
53.2 |
Local activities |
28. |
West Patel Nagar, Near Dr. Gore Lal Yadav, Residence |
56.3 |
--Do-- |
29. |
Mahesh Nagar, near Rajdhani Apartment |
56.4 |
--Do-- |
30. |
Shiv Puri Chuaraha, Near Shiv Mandir |
68.5 |
Traffic & Commercial activities |
31. |
Patliputra Colony in-front of Norte-Dame School. Patna |
52.3 |
Local activities |
32. |
Patliputra Colony main field, Near Sahyog hospital, Patna |
52.6 |
--Do-- |
33. |
South S.K. Puri Near Children Park |
67.1 |
Local activities as well as vehicular motion |
34. |
North S. K. Puri (Near Parmar coaching institute) |
50.7 |
Colony activities |
35. |
P&T Colony, Community Hall Kidwaipuri |
48.8 |
--Do-- |
36. |
S.K.Nagar (Infront of Bank of India) Road No.-25 |
51.3 |
--Do-- |
37. |
Indrapuri, Road no.-3, near Ankur Public School, Patna |
55.6 |
--Do-- |
38. |
East Patel Nagar(Near Gandhi Murti), Patna |
54.5 |
Local activities as well as Traffic |
39. |
Patel nagar Telephone office |
52.1 |
Local activities |
40. |
Rajbansi Nagar, Near Post Office |
54.5 |
--Do-- |
41. |
Kadam Kuan Golambar near Bihar Aurvedic College, Patna |
67.2 |
Traffic as well as local activities |
42. |
Rajendra Nagar, Near Magadh Hospital, Patna |
52.3 |
Local & Hospital activities |
43. |
Lohanipur main road near Shiv mandir, Patna |
71.1 |
Traffic congestion as well as local activities |
44. |
Mc Dowell Golumbar, Near Moinul Haque Stadium, Rajendra Nagar, Patna |
65.2 |
Traffic & local activities |
45. |
Kankarbagh, Bhootnath road, near Panitanki |
50.3 |
Local activities |
46. |
Kankarbagh near Central School, Patna-20 |
57.2 |
Traffic & Local activities |
47. |
In front of Gayatri Shakti Pith (Mandir), Kankarbagh-20 |
53.1 |
Local activities |
48. |
Kankarbagh Tempostand near 301&302 rental flat |
56.4 |
Traffic & Local activities |
49. |
Gardanibagh, Road No.- 4, Near Durbhash Kendra, Patna |
51.5 |
Local activities |
50. |
Gardanibagh Road No.- 15, Near Shishu Vidyamandir |
56.4 |
Traffic & Local activities |
51. |
Ranighat near professor Colony, Mahendru |
48.3 |
Colony activities |
52. |
Teacher’s Training College, Mahendru, Patna |
50.3 |
--Do-- |
53. |
Sultanganj near Devi Asthan, Patna |
62.4 |
Traffic & Local activities |
54. |
Guljarbagh near Hanuman Mandir, Patna city, Patna |
66.5 |
--Do-- |
55. |
Guru Ka Bagh Road, Near Girl’s School, Patna City |
53.2 |
Local activities |
Zone Category:Commercial Zone |
Day time Standards in respect of noise 06:00a.m.to10:00p.m:65dB(A) Leq |
56. |
Jagdeo Path Golumbar, Patna |
82.3 |
Traffic noise |
57. |
Raja Bazar near Petrol Pump, Patna |
85.5 |
--Do-- |
58. |
Sheikhpura More, Patna |
74.2 |
--Do-- |
59. |
Hartali Chouraha, Patna |
83.6 |
--Do-- |
60. |
Boring Road Crossing, Patna |
86.2 |
--Do-- |
61. |
Alapna Market, Patliputra |
73.4 |
--Do-- |
62. |
Patliputra Golumbar, Patna |
60.2 |
--Do-- |
63. |
Rajiv Nagar, Near Railway Crossing, Patna-24 |
64.3 |
Local as well as traffic activities |
64. |
Kurji More, Patna |
78.2 |
--Do-- |
65. |
Rajapur –Pul, Patna |
86.4 |
--Do-- |
66. |
Bansghat near Kali Mandir |
73.2 |
--Do-- |
67. |
Kargil Chowk, Gandhi Maidan |
81.3 |
--Do-- |
68. |
Ashok Raj Path near Patna Market |
83.1 |
--Do-- |
69. |
Mahendru Post Office, Patna |
83.4 |
--Do-- |
70. |
Kadam Kuan Golambar (Near St.Severin's High School), Patna-4 |
76.1 |
Traffic as well as local activities |
71. |
Hathua Market, Patna |
83.2 |
Traffic& Commercial activities |
72. |
Bari path Near in-front of Dariyapur Mosque), Patna |
76.4 |
Traffic& Commercial activities |
73. |
Machhua Toli Chowk (Bari Path Road), Patna |
81.6 |
--Do-- |
74. |
Bhikhana Pahari More, Patna |
82.3 |
--Do-- |
75. |
Musallahpur Hat, Patna |
73.5 |
Commercial activities |
76. |
Dinkar Golumbar, Nala Road(In front of Mandir) |
70.4 |
Traffic & Commercial activities |
77. |
Exhibition Road Crossing, Patna |
85.6 |
Traffic activities |
78. |
Dukbunlow Chouraha (Police Control Room), Patna |
85.4 |
--Do-- |
79. |
Maurya Lok near Sawmi Vivekanand Statue |
67.3 |
Commercial activities |
80. |
Infront of Hanuman Mandir (Patna Station), Patna |
86.8 |
Traffic& Commercial activities |
81. |
Bir Kunwar Singh Golumbar Near R. Block |
72.8 |
Road traffic noise |
82. |
Gardani Bagh, Near Chitkohra Market, Patna |
73.2 |
--Do-- |
83. |
Chirayatand Pul, Near Khas Mahal Road |
80.5 |
--Do-- |
84. |
Chirayatand Pul, Near Station Road |
78.6 |
Road traffic noise |
85. |
Kankarbagh near Rajendra Nagar overbridge |
82.4 |
Traffic& Commercial activities |
86. |
Bahadurpur Overbridge near Petrol Pump |
68.3 |
-- Do-- |
87. |
Agam Kuan Near Sitala Mandir. |
66.2 |
Local activities |
88. |
Patna City in front of Patna City Rly Station. |
75.5 |
Road traffic noise |
89. |
Patna City Chowk\ |
80.2 |
--Do-- |
90. |
Patna City, Bazar Chowk |
81.3 |
--Do-- |
Zone Category: Industrial Zone |
Day time Standards in respect of noise 06 :00 a.m. to 10:00p.m: 75 dB(A) Leq |
91. |
M/s Patliputra Industrial Estate, Near Shankar Motors Ltd. |
79.2 |
Vehicular service centre |
92. |
M/s Tata Engineering Autozone Services (P) Ltd. |
74.2 |
-- D0-- |
93. |
M/s Mahindra Authorised Dealer Kisanseva Kendra Service Centre, Patna-13 |
76.1 |
-- D0-- |
94. |
M/s Hindustan Coco Cola Beverages (P) Ltd. Patliputra Industrial Area, Patna-13 |
76.3 |
Industrial activities |
95. |
M/s Mahashakti Engineering Works, Industrial Area, Near Bridge Patna-13 |
62.3 |
-- D0-- |
96. |
M/s Natural Dairy-13,Patliputra Industrial Area |
80.2 |
-- D0-- |
97. |
M/s Ashoka Foundary, Patliputra Estate, Patna-13 |
63.2 |
-- D0-- |
[Note: dB(A) Leq represents the time weighted average of the level of sound in decibels on scale A which is relatable to the human hearing]
NOISE LEVEL ON DIWALI
A Report on Ambient Noise Level Monitoring is carried out as per CPCB Protocol given for Ambient Noise Level Monitoring in Patna town at Boring Road Crossing in normal day as well as on Diwali day, 2011.
Diwali is one of the important festivals of India and bursting of crackers and noise generating fireworks are integral part of its celebration. So generation of noise pollution and air pollution during the festival cannot be denied. Though the Hon'ble Supreme Court has banned the bursting of crackers or any noise generating fireworks of high decibels to control the noise pollution but unfortunately, the same is not being followed in letter and spirit. Therefore, an unbearable noise pollution creates severe problem to the common people during Diwali Festival.
Ambiant Noise Pollution Survey procédure:
Firecrackers generate instantaneous impulsive noise, which when measured in free field condition in impulsive mode, gives peak sound pressure level. It is quite obvious that a number of crackers when bursting serially can easily form a band of continuous noise in the presence of reflecting surfaces. The reverberation of sound wave due to repeated reflection in the surfaces prolongs the time interval of prevailing sound intensity. The continuous band of noise, thus formed, definitely affects the ambient level in close proximity.
The Integrating Sound Level Meter along with Microphone fitted with windscreen was placed 1.3m above the ground on the Tripod stand in the free field at Boring Road Crossing location. The site was appeared like free field. The monitoring point was away from obstacles. Data recorded at the said location for one-hour equivalent continuous noise level in Leq dB(A). The above procedure was repeated for 06 hours i.e.18:00 hours to 24:00 on normal day i.e. 19.10.2011 and the Diwali day i.e. on 26.10.2011 on the same location.
Bihar State pollution Control Board has conducted ambient noise level monitoring hourly at Boring Road Crossing, Patna for two days for 6 hours from 18:00 hours to 24:00 hours on normal day 19.10.2011 and on Deepawali day 26.10.2011 to observe the environmental impact of bursting of crackers. The observations were taken hourly. The observations of the monitoring are given in table below:
Ambient Noise Level at Boring Road Crossing in Patna during Normal and Diwali day in the year 2011
Location: Boring Road Crossing, Patna |
Normal Day(19.10.2011) |
Diwali Day (26.10.2011) |
Time Duration |
L min |
L max |
Leq dB(A) |
L min |
L max |
Leq dB(A) |
18:00 to 19:00 Hr. |
77.8 |
90.3 |
81.3 |
73.8 |
83.9 |
81.6 |
19:00 to 20:00 Hr. |
76.3 |
91.1 |
81.0 |
73.1 |
83.6 |
81.7 |
20:00 to 21:00 Hr. |
70.6 |
89.6 |
79.7 |
72.4 |
85.6 |
82.8 |
21:00 to 22:00 Hr. |
67.7 |
93.0 |
81.3 |
74.2 |
91.8 |
89.6 |
22:00 to 23:00 Hr. |
65.4 |
81.1 |
79.2 |
72.1 |
85.4 |
82.6 |
23:00 to 24:00 Hr. |
61.1 |
76.1 |
75.7 |
65.4 |
84.0 |
79.6 |
Day Time Average |
72.97 |
90.98 |
80.80 |
73.36 |
86.14 |
83.80 |
Night Time Average |
63.20 |
78.55 |
77.41 |
68.65 |
84.68 |
81.07 |
[Note: Monitoring site was commercial area.]
Findings of Ambient Noise Level Monitoring – Diwali- 2011
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The ambient noise level during day & night time at Boring Road Crossing on Diwali day- 2011 was found increased as comparedto normal day.
|
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The average ambient noise levels in day time for normal day were ranging from 72.97 to 90.98 in Leq dB(A) and on the eve of Diawali day 73.36 to 86.14 in Leq dB(A). |
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The average ambient noise levels in night time for normal day were ranging from 63.20 to 78.55 in Leq dB(A) and on the eve of Diwali day 68.65 to 84.68in Leq dB(A). |
Overall Conclusion:
Ambient Noise levels during day & night time on the occasion of Diwali Day, 2011 were found higher value with respect to the normal day, because of bursting of increased number of bursting crackers as well as from trade activities, the transport system and various domestic activities.
Recommendations:
I .
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The use of fireworks or firecrackers should not be permitted except between 6.00 p.m. and 10.00 p.m. No fireworks of firecrackers should be used between 10.00 p.m. and 6.00 a.m. |
II . |
Firecrackers should not be used at any time in silence zone. |
III . |
Appropriate steps should be taken to educate students about the ill effects of air and noise pollution. |
IV .
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The campaign against firecrackers should be initiated through Eco-Clubs of schools, which have taken up the issue in a big way by organising rallies and other programmes to create awareness among children in particular and the public in general on the ill-effects of crackers. The ill effects of noise pollution should also be displayed in slide show through Doordarshan and such thing should also be propagate among the people through Local Akashvani Kendra.
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Protecting The Common & Contribute to Peace and Quiet
A number of public complains are being made to the state pollution control board and local authority every month specially due to D.G. Sets, pressure horns and community hall for party & function. The following noise sources in the community can disturb quality of life:
» Music concerts and clubs.
» Car and home stereos. » Personal music players. » Bus, Truck, car, motor cycles and their pressure horn etc. and » Transportation: subways, traffic, garbage trucks.
There are several steps one can take to reduce noise in our community and protect us
► Turn down the volume: Today, many people play their television sets and personal stereos unnecessarily loud. keep the sound at safe level.
► Reduce your exposure: Some situations are inherently noisy, but you can decrease the risk of damage in several ways. Try to avoid going to loud bars, restaurants, or clubs for hours at a time. Limit the time you spend in noisy area;
► Protect yourself: Earplugs can be used to protect from noise and don’t be afraid to speak up for better hearing. Politely ask to turn it down.
► Remember your neighbors: Noise from your personal recreation affects not only you but everyone around you. Be a good neighbor and lower the volume. This is true whether at home, the beach, or a shopping mall—anywhere your loud noises could interfere with others’ peace
► Use silent generator only, and
► Educate your children: Educate and talk to your children about what is noise and their health hazards.
To learn more please visit the following external links:
₪ NoisePollution:Sources,Effectsand Control
₪ DecibelTable − Loudness Comparison Chart
₪ Conversion of sound units (levels)
₪ Sound (music) and noise (bang)
₪ The Relation of Sound Quantities-their Levels and References. Conversions, Calculations and Formula
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