kebisingan industri
DESCRIPTION
Kebisingan Industri. Definisi dan pengertian. Bising = suara-suara yang tidak dikehendaki Definisi secara ilmiah = sensasi yang diterima telinga sebagai akibat fluktuasi tekanan udara ‘superimposing’ tekanan atmosfir/udara yang steady - PowerPoint PPT PresentationTRANSCRIPT
Kebisingan Industri
Definisi dan pengertian
Bising = suara-suara yang tidak dikehendaki
Definisi secara ilmiah = sensasi yang diterima telinga sebagai akibat fluktuasi tekanan udara ‘superimposing’ tekanan atmosfir/udara yang steady
Bising = sejenis vibrasi/energi yang dikonduksikan dalam media udara, cairan, padatan, tidak tampak, dan dapat memasuki telinga serta menimbulkan sensasi pada alat dengar
Inside NOISE
What is noise?– Definition, energy conducted and sensed, properties:
intensity/pressure, frequency, exposure,
Why unwanted?– Health Effect, age, psychological: annoyed, concentration,
rest/relax problem, communication annoyance, physiological: blood, heart, hearing loss, nausea, muscle control, acoustic trauma (permanent) vs temporary,
Who are susceptible? – Esp. Industrial workers, determining factors: sensitivity,
age,
How to evaluate & control?
What is noise?
Definisi: Suara-suara yang tidak dikehendaki (for
Who? Why?)Suara: sensasi yang diterima telinga
sebagai akibat fluktuasi tekanan udara terhadap tekanan udara yang stabil.
Telinga akan merespons fluktuasi-fluktuasi kecil tersebut dengan sensitivitas yang sangat besar.
Properties of noise?
Karakteristik bising
1. Intensitas/tekanan (sound pressure/intensity)
2. Frekuensi3. Durasi eksposur terhadap bisingKetiga karakteristik diperlukan karena: Semakin keras suara, semakin tinggi
intensitasnya Frekuensi tinggi lebih berbahaya
terhadap kemampuan dengar. Telinga manusia lebih sensitif terhadap frekuensi tinggi
Semakin lama durasi eksposur semakin besar kerusakan pada mekanisme pendengaran
Jenis BisingTergantung pada durasi dan frekuensiSteady wide band noise, bising yang
meliputi suatu jelajah frekuensi yang lebar (bising dalam ruang mesin)
Steady narrow band noise, bising dari sebagian besar energi bunyi yang terpusat pada beberapa frekuensi saja, contoh gergaji bundar.
Impact noise, kejutan singkat berulang, contoh riveting
Intermitten noise, bising terputus, contoh lalu lintas pesawat
Contoh…
Tekanan = Sound Pressure
Manusia dapar mendengar suara pada tekanan antara 0,0002 dynes/cm2 (ambang dengar/threshold of hearing) sampai 2000 dynes/cm2 range besar sehingga satuan yang dipakai dB (decibel): logaritmik
Dinyatakan dalam decibel (dB) yang dilengkapi skala A, B, dan C sesuai dengan berbagai kegunaan
Skala A digunakan karena merupakan response yang paling cocok dengan telinga manusia (peka terhadap frekuensi tinggi)
Skala B dan C untuk evaluasi kebisingan mesin, dan cocok untuk kebisingan frekuensi rendah
Intensitas
Laju aliran energi tiap satuan luas yang dinyatakan dalam desibell (dB) – Alexander Graham Bell-
dB adalah merupakan satuan yang dihasilkan dari perhitungan yang membandingkan suatu tekanan suara yang terukur terhadap suatu tekanan acuan (sebesar 0,0002 dyne/cm2).
B = log (int.terukur/int.acuan) untuk mendapatkan angka yang lebih akurat ditentukan dengan angka kelipatan 10 (desi)
Intensity level dB=10 Log (IT/IA)Sound pressure level (tekanan bunyi) = 20
log (IT/IA), karena intensitas sebanding dengan kuadrat tekanan bunyi.
Ruang kelas: ?dB Rumah Restauran Berbisik Berteriak Jet plane
The decibel
SOUND INTENSITY
SOUND SOURCE LINEAR UNITS Bel
LOGARITHMIC UNITS Decibel
Lowest limit of hearing 1 0 0
Rustling leaf 10 1 10
Quiet farm setting 100 2 20
Whisper (5 feet) 1,000 3 30
Dripping faucet, quite office 10,000 4 40
Low conversation, residence 100,000 5 50
Ordinary conversation 1,000,000 6 60
Idling car 10,000,000 7 70
Silenced compressor, very noisy restaurant 100,000,000 8 80
Backhoe 1,000,000,000 9 90
Unsilenced compressor 10,000,000,000 10 100
Rock dril, woodworking 100,000,000,000 11 110
Pile driver* 1,000,000,000,000 12 120
Rivet gun* 10,000,000,000,000 13 130
Explosive-actuated tool*, jet plane 100,000,000,000,000 14 140*Intermittent or "impulse" sound
Source: Construction Safety Association of Ontario, Hearing Protection for the Construction Industry, 1985, page 3
The decibel
dB = 10 log10 (I1/I0) I = Intensitas
dB = 20 log10 (P1/P0) P= Tekanan = 0,0002 dynes/cm2
SP (microbar) SPL (dB) Ratio Intensitas
0,0002 0 100
0,002 20 102
Jadi bila SP berubah 10x, maka dB bertambah ? x
PressurePa Bel (B) Decibel (dB)
Threshold of hearing 0,00002 0 0Quiet office 0,002 4 40Ringing alarm clock at 1 m 0,2 8 80Ship's engine room 20 12 120Turbo jet engine 2000 16 160
Sound intensities
Frekuensi
Adalah jumlah getaran dalam tekanan suara per satuan waktu (Hertz atau cycle per detik), frekuensi dipengaruhi ukuran, bentuk dan pergerakan sumber, pendengaran normal orang dewasa dapat menangkap bunyi dengan frekuensi 20-15.000 Hz.
Frekuensi
Dibagi dalam 8 octaf (octave bands), 37.5, 75, 150, 300, 600, 1200, 2400, 4800, 9600 Hz
Telinga manusia bereaksi beda terhadap berbagai frekuensi
Kebisingan ‘rata-rata’ mencakup seluruh taraf kebisingan dari setiap frekuensi dihitung LeqLeq = ekuivalen noise level/ekuivalen energi level
Leq = 10 log10 (Σ 10 Lpi/10)
Satuan (Konversi)
1bar=105Pa=105N/m2
=105.105dyne/104cm2
=106dyne/cm2 atau1microbar = 1 dyne/cm2
Sumber > 1…..
dB=L=20 log(P1/P2)=10 log(P1/P2)2
L/10= log(P1/P2)2
10L/10= 10log(P1/P2)^2=(P1/P2)2
L=10 log(P1/P2)2
=10 log 10L/10 (satu sumber)
L =10 log (Σ10Li/10) (sumber banyak)
=10 log (10L1/10+ 10L2/10+…)
Sumber > 1….. (Contoh)
=10 log (Σ10Li/10) (banyak sumber)
=10 log (10L1/10+ 10L2/10+…)
Perbedaan antara sumber
bunyi
ΣdBA yang turun ditambah ke
bunyi terbesar
0 3,0
1 2,6
2 2,1
3 1,8
4 1,5
5 1,2
6 1,0
7 0,8
8 0,6
10 0,4
12 0,3
14 0,2
16 0,1
Satuan (Konversi)
1bar=105Pa=105N/m2
=105.105dyne/104cm2
=106dyne/cm2 atau1microbar = 1 dyne/cm2
Sumber > 1…..
dB=L=20 log(P1/P2)=10 log(P1/P2)2
L/10= log(P1/P2)2
10L/10= 10log(P1/P2)^2=(P1/P2)2
L=10 log(P1/P2)2
=10 log 10L/10 (satu sumber)
L =10 log (Σ10Li/10) (sumber banyak)
=10 log (10L1/10+ 10L2/10+…)
Sumber > 1….. (Contoh)
=10 log (Σ10Li/10) (banyak sumber)
=10 log (10L1/10+ 10L2/10+…)
Perbedaan antara sumber
bunyi
ΣdBA yang turun ditambah ke
bunyi terbesar
0 3,0
1 2,6
2 2,1
3 1,8
4 1,5
5 1,2
6 1,0
7 0,8
8 0,6
10 0,4
12 0,3
14 0,2
16 0,1
Kebisingan dari 2 sumber
14Perbedaan antara 2 tingkat bising, dB(A)
3
2,5
12108642
0,5
1,5
2
1
Dec
ibel
yan
g di
tam
bahk
an p
ada
tingk
at k
ebis
inga
n le
bih
tingg
i
Perbedaan (dB)
Tambah pada yg lebih tinggi
0 atau 1 3
2 atau 3 2
4 – 9 1
10+ 0
Why unwanted?
Health Effect, age, psychological: annoyed, concentration, rest/relax problem, communication annoyance, physiological: blood, heart, hearing loss, nausea, muscle control, acoustic trauma (permanent) vs temporary,
Efek bising pada manusia Psikologis, terkejut, mengganggu
dan memutuskan konsentrasi, tidur dan saat istirahat
Fisiologis, seperti menaikkan tekanan darah dan detak jantung, mengurangi ketajaman pendengaran, sakit telinga, mual, kendali otot terganggu, dll.
Gangguan komunikasi yang mempengaruhi kenyamanan kerja dan keselamatan.
Interference with communication by speech
When background or ambient noise levels are sufficiently high enough, the background noise can mask the sound levels of speech that wish to be heard.
Restaurants can often be classic examples of excessive noise interference due to lack of sufficient quality or quantity of sound absorbing materials that prevent excessive noise buildup.
Diners have to speak louder and louder to be heard and in doing so compete with one another, thereby increasing the sound levels to even greater levels. Appropriate acoustical treatment will prevent the reflected noise buildup and significantly reduce the necessity for diners to speak louder to enjoy conversations with one another.
Mechanics of hearing
Mekanisme pendengaran
• Terdiri dari 3 bagian: telinga luar (daun telinga sampai membran timpani) meneruskan gelombang ke telinga tengah
• Telinga tengah: membran timpani (yang melekat pada 3 tulang kecil sampai membrana ovale) getaran diteruskan
• Telinga dalam: tube berspiral seperti rumah siput berisi cairan cairan bervibrasi stimulasi rambut sel impuls syaraf otak
Gangguan pendengaran
Pemaparan pada suara tinggi dan periode/durasi yang lama akan menyebabkan sel syaraf pendengar dan rambut pada corti over aktif sehingga menimbulkan kehilangan pendengaran permanen
Pengukuran kebisingan
• Mengukur overall level sound level meter (satuan dBA)
• Mengukur kebisingan pada setiap level frekuensi SLM dengan frequency analyzer
• Penentuan eksposur kebisingan padapekerja noise dosimeter (satuan dBA)
Alat ukur
Sound level meter, mencatat keseluruhan suara yang dihasilkan tanpa memperhatikan frekuensi yang berhubungan dengan bising total (30-130 d) – (20-20.000Hz)
Sound level meter dengan octave band analyzer, mengukur level bising pada berbagai batas oktaf di atas range pendengaran manusia dengan mempergunakan filter menurut oktaf yang diinginkan (narrow band analyzers untuk spektrum sempit 2-200 Hz)
NOISE KALIBRATOR
SOUND LEVEL METER
NOISE MEASUREMENT KIT
NOISE DOSIMETER
PENGUKURAN PADA PEKERJA
DOSEBADGER
Construction Noise Levels
Pneumatic chip hammer
103-113 Crane 90-96
Jackhammer 102-111 Hammer 87-95
Concrete joint cutter
99-102 Gradeall 87-94
Skilsaw 88-102Front-end loader
86-94
Stud welder 101 Backhoe 84-93
Bulldozer 93-96Garbage disposal (at 3 ft.)
80
Earth Tamper 90-96Vacuum cleaner
70
Construction Noise Levels
Pengukuran akibat bising
Untuk mengevaluasi akibat pemaparan terhadap kehilangan pendengaran, kenyamanan, interferensi komunikasi dan mengumpulkan informasi untuk pengontrolan.
How Does Excessive Noise Damage Your Ears? Microscopic hair cells of the cochlea are
exposed to intense noise over time Hair cells become fatigued and less responsive,
losing their ability to recover. Damage becomes permanent resulting in noise-
induced permanent threshold shift. Risk of Hearing Loss Estimated Risk of Incurring Material Hearing
Impairment as a Function of Average Daily Noise Exposure Over a 40-year Working Lifetime (source: NIOSH)
Average Exposure 90 dBA 29% Average Exposure 85 dBA 15% Average Exposure 80 dBA 3%
Ketulian
= berkurangnya ketajaman pendengarandibanding/terhadap orang normal (15 dB)/ gol usia
• Ada 2 macam: - permanen: karena penyakit, usia tua, obat, trauma, dankebisingan- temporer: akibat ekposur bising, dapat pulih setelahistirahat beberapa saat tergantung keparahan
• Ketulian temporer akan menjadi permanen bila terusterekpos bising (dari rumah, tempat umum, rekreasi, musik, industri, dll.)
• Secara mekanisme: ketulian ada 2:- konduktif: peralatan konduksi suara rusak akibattrauma atau sakit- sensorinueral: akibat persyarafan pendengaran rusak
Audiometric test
Audiometric test
Audiometric test
Current OSHA Standards •1926.52 Occupational Noise Exposure
•TABLE D-2 - PERMISSIBLE NOISE EXPOSURES
Duration per day, hoursSound Level dBA slow response
8 90
6 92
4 95
3 97
2 100
1 1/2 102
1 105
1/2 110
1/4 or less 115
What Is The Purpose of Having a Hearing Test on a Regular Basis?
An audiometric testing program is used to track your ability to hear over time. – Baseline and annual
Test records provide the only data that can be used to determine whether the program is preventing noise-induced permanent threshold shifts. It is an integral part of the hearing conservation program.
Case Study 1. Teenage Girl From the American Academy of Family Physicians website, Rabinowitz article
FIGURE 1. Audiogram findings in the patient in case 1.
The area below the curves represents sound levels that the patient could still hear. (X = left ear; O = right ear)
Case Study 1 Conclusion
"Temporary threshold shift" example Common in persons exposed to high
noise Represents transient hair cell
dysfunction Complete recovery can occur Repeated episodes of such shifts
causes permanent threshold shifts because hair cells in the cochlea are progressively lost.
Case Study 2 Factory Worker Age 55
Case Study 2 Conclusion Noise Induced Hearing Loss
– Speech discrimination and social function interference
– Difficulty in perceiving and differentiating consonant sounds
– Sounds such as a baby crying or a distant telephone ringing, may not be heard at all.
Tinnitus – Common symptom of noise overexposure – Further interferes with hearing acuity, sleep and
concentration. These impairments have been associated with
depression and an increased risk of accidents.
Carpenter Hearing Losses by Age
Damage risk criteria
Variation in individual susceptibilityThe total energy of the soundThe frequency distribution of the soundOther characteristics of the noise
exposure, such as whether it is continuous, intermittent, or made up of a series of impacts
The total daily time of exposureThe length of employment in the noise
environment.
Noise control
A source radiating sound energyA path along which the sound
energy travelsA receiver such as the human ear
Pengendalian kebisingan
Pengendalian dilakukan di 3 bagian: SUMBER, RUANG ANTARA sumber dan penerima/pekerja, pada PENERIMA/PEKERJA
Urutan pengendalian paling efektif:
• Kurangi/hilangkan sumber bising
• Pengendalian pathway: jarak diperjauh dengan perisai/isolator/automatisasi
• Perlindungan penerima dari bising (APD)
SUMBER PATHWAY/MEDIA PENERIMA/RECEIVER
•Cara teknis:
APDPerpanjang jarak
Reduksi waktuPerisaiInsulasi sumber
Isolasi pekerjaAbsorpsi/dampingSubstitusi
PENERIMAPATHWAYSUMBER
•Cara medis:Pemeriksaan ketajaman pendengaran secara periodikPenempatan pekerja sesuai dengan kepekaan thd bisingMonitor ketulian temporer
•Cara manajemen:Reduksi waktu eksposurDiklat pemakaian dan pemeliharaan APD
Noise control
Source: modification or redesigning of the source.– The modification of compressed air jets for
parts
ejection, to reduce noise by altering the jet flow.– Multiple-opening air ejection nozzel: less
noise than
single-opening.
Noise controlNoise can be controlled at the source, along the
path or at the worker. At the source, equipment may be replaced by
quieter models, or less noisy work procedures can be adopted. - In general, less friction and vibration mean less noise. Maintenance procedures such as lubrication may sometimes reduce noise by reducing friction. - Equipment can sometimes be modified to reduce the amount of noise that is generated. Sound-absorbing material may be attached to the noise source. Or the frequency of the noise may be shifted to one that is less hazardous.
Noise controlNoise can often be controlled along the
path to the worker with:- the use of sound-absorbing paneling on walls or ceilings, and - enclosures around noisy machinery.
Controls at the worker include both administrative controls and personal protective equipment. – Administrative controls modify how the work
is carried out. – The time employees spend in noisy areas may
be reduced. – Workers in noisy areas may be rotated to less
noisy areas.
As the distance from the noise source increases, the pressure (or intensity) of the noise decreases faster than its sound level.
Noise control
Noisy operations may be conducted outside normal working hours to reduce the number of people exposed.
Where noise exposures cannot be reduced by other methods, hearing protection is required. This includes ear plugs and ear muffs.
Insulation of the workers
A separate noise insulated room provides effective control (up to 30 dB noise reduction).
Machine insulation
Machine: on floors and walls vibrate themsound radiation
proper use of machine mountings insulates the machine and reduce the transmission of vibration
Control of noise by absorption
Travels out in all directionWhen encounter wallsreflectedTotal noise exposure within the
room = direct + reflected noiseApplication of sound absorption
material (However, limited: no effect on direct noise).
Reduction of exposure time
Limiting the total daily exposure reduces the noise hazard.
See TLV
Personal protection against noise
Many operations cannot be quieted by engineering methods.
Therefore protection: ear plugsProperly worn: 25 – 400 dB
protectionDegree of discomfort employee
education is adequate
Example….
Durasi tingkat bising yang diijinkan dapat dilihat dari tabel di bawah ini:
Kebisingan yang terukur di suatu area adalah 90 dB selama 2 jam sehari, 97 dB selama 2 jam, dan sisa 4 jam berikutnya terdapat variasi tingkat bising secara bergantian 95 dB selama 10 menit dan 80 dB selama 10 menit. Tentukan apakah tingkat kebisingan yang terukur masih dalam batas yang diijinkan atau tidak.
Durasi per hari
Tingkat bising
86432
1,51¾½¼
90929597
100102105107110115
Faktor-faktor yang mempengaruhi bising
Tipe bising: menerus dan terputus
Lokasi pekerjaWaktu kerja
NAB Kebisingan di lingkungan kerja
USA (TLV ACGHI)t (eksposur) jam dB(A)
8 906 924 953 972 100
1,5 1021 105
0,5 110<0,25 115
kebisingan impulsif < 140 dB
t dBA8 854 882 911 94
30 mnt 9715 mnt 1007,5 mnt 103
3,75 mnt 1061,88 mnt 109
dstdilarang > 140 dB
INDONESIA Permen 51/1999
Waktu pemaparan vs dB (TLV)
Waktu pemaparan (jam)
dB
8642
1,51
0,5<0,25
909295100102105110115
(Sumber: FHI)
Steps aiming to control noise at workAssess risks to develop a noise
control planReduce risks for all employeesInvestigate and implement good
practice for control of noise Prioritise noise control measures Use hearing protection for residual
risksCarry out a noise dosimetry
program to check the effectiveness of noise control measures
Some simple noise control techniquesApplication of damping material
to chutes, hoppers, machine guards etc., can give a 5-25 dB reduction in the noise radiated
Cabin internal noise can be reduced by 10-12 dB by applying damping pads and sound barrier mats to floor and engine bulkhead
Reduce fan speed by 30% to achieve a noise reduction of 8 dB
BARRIER-BARIER ATAU PANEL
ISOLASI PEKERJA/MESIN DI TEMPAT BISING
BAHAN ABSORBER BAHAN BARRIER
Noise control can be complex
Use noise control consultants to help solve your problems if complex
Engage employees in process
Hearing protectors
Selected for protection, user preference and work activity
Guard against over-protection — isolation can lead to under-use and safety risks
Require information, instruction, training, supervision and motivation
Will only protect if worn all the time and properly
Rating hearing protectors
The sound level conversion (SLC80 ) rating of a
hearing protector, ear plugs or headset is a simple
number and class rating that is derived from a test
procedure as outlined in the Australian/New Zealand
Standard AS/NZS 1270:2002
Class and specification of hearing protectors
SLC80Class May be used up to this
noise exposure level
10 to 13 1 90 dB(A)
14 to 17 2 95 dB(A)
18 to 21 3 100 dB(A)
22 to 25 4 105 dB(A)
26 or greater
5 110 dB(A)
Ear plugs
Properly fitted Wrongly fitted
Ear muffs
Proper clamping force
Worn-out head band
Reduction in protection provided by hearing protectors with decreased wearing time
Example: Effectiveness of wearing an ear muff with a rating of 30 dB for an exposure time of one hour
Wear timeEffective
attenuation
60 minutes 30 dB
55 minutes 11 dB
50 minutes 8 dB
45 minutes 6 dB
Our challenge
Away from …Noise assessment as the end
pointReliance on hearing protectionTowards …Control of noise risks through
prioritised action plansIntroducing equipment with good
noise and vibration characteristics – ‘Buy Quiet’
TWA untuk kebisingan: berdasarkan standar kebisingan.
Jumlah jam dB(A)
1,5 102
1,0 105
0,75 107
0,5 110
0,25 115
Jumlah jam dB(A)
8 90
6 92
4 95
3 97
2 100
dB(A) 80 90 95 97 100
1 T ukur 2 jam 4 jam 2 jam
T TLV tt 8 jam 4 jam 3 jam
TWA 0 4/8 2/4 = 1 < batas aman
2 T ukur 0 2 jam 2 jam 2 jam
T TLV tt 8 jam 4 jam 3 jam
TWA 0 2/8 2/4 2/3 = 17/12 >batas aman
STANDAR KEBISINGAN
Noise3. 4 orang pekerja printer di unit percetakan dimana terdapat
offset press. Masing-masing terpapar sbb:
Berapa dosis harian yang diterimanya? dan Equivalent 8-hour Sound Pressure Level (SPL) yang dialami pekerja percetakan tersebut?
No. of presses operating
Average Sound Pressure Level (dBA)
Average daily time in operation
(hours)
0 81 4.5
1 93 2.1
2 96 1.0
3 98 0.4
Jawab:
5/)90(max 2
8
LT
5/)9081(max 2
881@ dBAT = 27.858 jam
Untuk SPL 81 dBA:
5/)9093(max 2
893@ dBAT = 5.278 jam
Untuk SPL 93 dBA:
5/)9096(max 2
896@ dBAT = 3.482 jam
Untuk SPL 96 dBA:
5/)9098(max 2
898@ dBAT = 2.639 jam
Untuk SPL 98 dBA:
Noise
niT
C
T
C
T
C
T
CD n
n
i
i
max1 max
2
max
1
max
....21
639.2
4.0
482.3
0.1
278.5
1.2
858.27
5.4int erprD = 0.998
Now, expressing this result as a percentage as required by the problem statement, we have: Dprinter= 99.8%
The Printing Company that employs these four Printers is not in violation of any established OSHA SPL dosage standards.
Noise
Lequivalent = 90 + 16.61 log[D]
Lequivalent = 90 + 16.61 log[0.998] = 89.987 ~ 90 dBA
These Printers experience an equivalent SPL of ~ 90 dBA
Noise
4. How much longer is an individual, without hearing protection, permitted to work at a location where the noise level has just been reduced from 104 dBA to 92 dBA?
To answer this question, we must first determine the OSHA permitted duration, in hours, for each of the two identified noise levels.
Tmax = 8 / [2(L-90)/5]
For an SPL of 104 dBA: Tmax @ 104 dBA= 8 / [2(104-90)/5] = 1.149 hours
For an SPL of 92 dBA: Tmax @ 92 dBA= 8 / [2(92-90)/5] = 6.063 hours
The additional time permitted at the lesser noise level of 92 dBA, ΔTmax, is simply the difference between these two OSHA permitted time intervals; thus:
ΔTmax=6.063 – 1.149 = 4.914 hours
This individual can spend an additional 4.9 hours at a 92 dBA noise level