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    STUDY OF NOISE POLLUTION

    DURING HAJJ SEASON 1427 H

    Senior Project Report

    Submitted to

    Umm Al-Qura University

    College of Engineering & Islamic Architecture

    In Partial Fulfillment Of The Requirements ForBachelor Degree Of Mechanical Engineering

    Supervised By:

    Dr. Muhammed Al-Hazmi

    Dr. Hamza Ghulman

    Dr. Abdulaziz Al-Seroji

    Prepared By:Abdulaziz Al-Zahrani 42302596

    Hazim Al-Hazimi 42302547

    Rami Menkabo 42303806

    Meshal Al-Malki 42303454

    Muhammed Al-Mutairi 42302645

    Mutaz Qutob 42205233

    Submitted at

    Shaaban 1428 H

    August 2007 D

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    APPROVED BY:

    Dr. Abdulaziz Al-Seroji.

    Dr. Muhammed Al-Hazmi.

    Dr. Hamza Ghulman.

    Dr. Talal Mandourah.

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    I

    ABSTRACT

    This study is a result of cooperation work between mechanical

    engineering department and the Custodian of the Two Holy Mosques

    Institute of Hajj Research to evaluate the noise level in a holy Mina valley

    and Arafat area during hajj season in 1427 H. This is being carried out as

    a part of the Saudi Arabia government future plan to develop the holy lands.

    It has been created for the purpose of providing information on the level of

    noise across the Mina valley and Arafat area. Sound level meters were

    used to measure noise level in the selected places at a certain period of time

    by using broadband mode (time and location of measurements were

    selected according to hajj rites) . The obtained data was manipulated in

    scientific manner and then compared with world health organization

    standard. Results showed that noise annoyance is acceptable in all

    measured areas except noise around Jamarat, because the level of noise in

    that area exceeds normal standard and it may affect people there .

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    II

    ACKNOWLEDGMENT

    Authors would like to think and present their gratitude to the

    Custodian of the Two Holy Mosques, Institute of Hajj Research, university

    of Umm Al-Qura, Makkah for their financial support in this study. We

    would also like to thank Dr. Abdulaziz Seroji , a director of department of

    Environmental and Health Research at the institute for his encouragement

    and personal interest in this project. Indeed it would not have been possible

    to complete the project without his help and from time to time guidance.

    Thanks are also due to all those working in The Custodian of the Two Holy

    Mosques, Institute of Hajj Research who helped the authors in many ways

    at various occasions. Our great acknowledgments for Dr. Muhammed Al-

    Hazmi and Dr. Hamza Ghulman for helping us in the project . Finally,

    many thanks for all those help us in order to take the measurements during

    Hajj season 1428H .

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    III

    TABLE OF CONTENTS

    Topic Page

    Abstract IAcknowledgment. II

    Table of Contents .III

    List of illustrations... .... VII

    List of Tables .... XList of symble and technical tearms... XI

    Chapter 1 Introduction ......................................................................... 1

    1 Introduction ................................................................................... 21.1 Background ............................................................................ 21.2 The Importance of Study .......................................................4

    1.3 Objectives of Study ................................................................71.4 The outlines of the study ........................................................8

    Chapter 2 Physics of Sound and Human Ear ..................................... 112 Human Ear and Physics of Sound .............................................. 12

    2.1 The Human Ear .................................................................... 122.2 Frequency Response Curves ................................................ 16

    2.3 Physics of sound................................................................... 172.3.1 Sound ............................................................................. 172.3.2 Noise .............................................................................. 18

    2.3.3 Speed of Sound .............................................................. 192.3.4 Sound Characteristics .................................................... 20

    Chapter 3 Literature Review .............................................................. 263 Literature Review........................................................................ 27

    3.1 The Studies ........................................................................... 273.2 Effict of noise ....................................................................... 31

    Chapter 4 Instrumentation ................................................................. 354 Instrumentation ........................................................................... 36

    4.1 Introduction ......................................................................... 364.2 Specifications ...................................................................... 36

    4.3 Measurement Functions ....................................................... 374.3.1 BroadBand Measurement Mode .................................... 374.3.2 Octave Band Measurement ............................................ 38

    4.4 Sound Level Meter Calipration ........................................... 384.5 The mesurement duration .................................................... 394.6 The Measurement Auto-Repeat ........................................... 404.7 The measurement Auto- Synchronise .................................. 40

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    IV

    4.8 Measurement Range ............................................................. 414.9 Windshield ........................................................................ 424.10 The Batteries ..................................................................... 44

    4.11 Configuring the Sound Level Meter ................................ 454.12 Menu System .................................................................... 474.13 Viewing and downloading the measurement .................. 474.15 Maintenance and Care ...................................................... 51

    Chapter 5 Scope of Work .................................................................. 535 Scope of Work ............................................................................ 54

    5.1 Mina Valley ......................................................................... 54

    5.1.1 King Fahad street .......................................................... 545.1.2 King Abdulaziz Street ................................................... 55

    5.1.3 Jamarat Bridge ................................................................ 555.1.4 King Abdulaziz Bridge ................................................. 575.1.5 Al-Kheef Mosque .......................................................... 58

    5.2 Arafat Area .......................................................................... 59

    5.2.1 Namirah Hospital .......................................................... 595.2.2 Namerah Mosque .......................................................... 595.2.3 Al-Rahmah Mountain .................................................... 605.2.4 Al-Rahmah Hospital ...................................................... 605.2.5 Pedestrian Way .............................................................. 615.2.6 Road NO. 4 .................................................................... 61

    5.2.7 Road NO. 8 ..................................................................... 625.2.8 Taradodiah ..................................................................... 62

    Chapter 6 Results and Discussion ..................................................... 636 Results and Discussion ............................................................... 64

    6.1 Som Hajj Rites ..................................................................... 64The 8thof Dulhijja (Tarwiah Day) ................................. 64The 9thof Dulhijja (day of Arafat) ................................ 64

    The 10thof Dulhijja (day of al-Nahr) ............................ 65The 11thof Dulhijja (The First day of Tashriq days).65

    The 12

    th

    of Dulhijja (The second day of Tashriq days) ............................................................................................. 65The 13thof Dulhijja (The third day of Tashriq days).65

    6.2 Calculation ......................................................................... 66

    6.3 Mina Valley ......................................................................... 666.3.1 King fahad Street ............................................................ 66

    The 8thof Dulhijja (Tarwiah Day)( 28/12/2006) ............ 66

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    V

    6.3.2 King Abdulaziz Street .................................................... 67The 8thof Dulhijja (Tarwiah Day)( 28/12/2006) ............ 68The 9thof Dulhijja (day of Arafat)( 29/12/2006) ........... 69

    The 11thof Dulhijja (The first day of Tashriq days)( 31/12/2006) ......................................... 70

    The 12thof Dulhijja (The second of Tashriq days )

    ( 01/01/2007) .................................................. 71The 13thof Dulhijja (The third of Tashriq days)

    ( 02.01/2007): ............................................. 72Over View of Level Noise in King Abdul Aziz Street

    ........................................................................................ 736.3.3 King Abdulaziz Bridge .................................................. 74

    The 8

    th

    of Dulhijja (Tarwiah Day)( 28/12/2006) ............ 74The 9thof Dulhijja (day of Arafat)( 29/12/2006) ........... 75The 10thof Dulhijja (The first day of Tashriq days)

    ( 30/12/2006) ................................................... 76

    The 11thof Dulhijja (The second of Tashriq days )( 31/01/2007) ................................................. 77

    The 12thof Dulhijja (The third of Tashriq days)( 01.01/2007): ............................................ 78

    Over View of Level Noise in King Abdul Aziz Bridge........................................................................................ 79

    6.3.4 Jamarat Bridge, Ground floor ........................................ 79The 10thof Dulhijja in (30/12/2006)( Jamrat Al-Aqaba ) ..

    ........................................................................................ 80The 11thof Dulhijja (The first day of Tashriq days)

    in (31/12/2006) (Al- Jamrah Al-Wasta ) .............................. 81The 12thof Dulhijja (The second day of Tashriq days)

    in (01/01/2007) (Al-jamrah Al-sughra ): .............................. 82

    The 13thof Dulhijja (The third day of Tashriq days)

    in (02/02/2007) (Jamrat Al-Aqaba ): .................................... 83

    Over View of Level Noise in Jamarat Ground Bridge........................................................................................ 846.3.5 Jamarat Bridge , First Floor ........................................... 85

    The 10thof Dulhijja in (30/12/2006)( Jamrat Al-Aqaba )

    ........................................................................................ 85The 11thof Dulhijja (The first day of Tashriq days)

    in (31/12/2006) (Al- Jamrah Al-Wasta ) .............................. 86

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    VI

    The 12thof Dulhijja (The second day of Tashriq days)in (01/01/2007) (Al-jamrah Al-sughra ) ................................ 87

    The 13thof Dulhijja (The third day of Tashriq days)

    in (02/02/2007) (Jamrat Al-Aqaba ) ..................................... 88Over View of Level Noise in Jamarat Bridge,First Floor........................................................................................ 89

    6.3.6 Alkhaif Mosque : ................................................................. 90The 8thof Dulhijja (Tarwiah Day)( 28/12/2006) ............ 90The 9thof Dulhijja (day of Arafat)( 29/12/2006) ........... 91The 10thof Dulhijja (The first day of Tashriq days)

    ( 30/12/2006) .................................................. 92Over View of Level Noise in Alkhaif Mosque .............. 93

    6.4 Arafat Area : (The 9

    th

    of Dulhijja (Arafah Day)( 29/12/2006). ........................................................ 946.4.1 AL-Rahmah Hospital ..................................................... 946.4.2 AL-Rahmah Mountain ................................................... 95

    6.4.3 Namerah Hospital ........................................................... 966.4.4 Namerah Mosque ........................................................... 976.4.5 Road No.4 ....................................................................... 986.4.6 Pedestrian ....................................................................... 996.4.7 Road No. 8 .................................................................... 1006.4.8 Tradodiah...................................................................... 101

    6.4.9 Over View of Level Noise in Arafat ............................ 1026.5 The Main Source of Noise in The Hajj Season ................. 104

    6.5.1 Motorcycle ................................................................... 1046.5.2 Civil Defense ................................................................ 105

    Civil Defense car Alarm ( 1 ) ...................................... 105Civil Defense car Alarm ( 2 ) ...................................... 106

    6.5.3 Fans of Tunnel .............................................................. 107

    6.5.4 Cars ............................................................................... 1086.5.5 Buses ............................................................................ 109

    6.5.6 Ambulance ................................................................... 1106.5.7 Truck of water .............................................................. 1116.5.8 Over View of Level Noise ........................................... 112

    Chapter 7 Conclusion And Recommendations ................................ 114

    7 Conclusion And Recommendations ......................................... 115Refrences ........................................................................................ 116Appendices ....................................................................................... 118

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    VII

    LIST OF ILLUSTRATIONSPage

    Figure 2-1 :The Human Ear... 13Figure 2-2 :Frequency Response Curve ... 17

    Figure 2-3 : Spatial pressure distribution in a plane wave at one

    instant of time 22

    Figure 4 -1 : Noise The status of the different functions.. 39Figure 4 -2 : The Run Duration of the measurement defined. 41

    Figure 4 -3 :The Windshield Foam 43

    Figure 4 -4 : The positions of the Batteries... 44Figure 4 -5 : The Keypad of the instrument. 45Figure 4 -6 : The Deaf Defier3 software 48

    Figure 4 -7 : The space of the different measurements of theinstrument. .. 49

    Figure 4 -8 : The space of the different measurements of theInstrument..

    50

    Figure 5-1 :Mena Valley (1)... 56Figure 5-2 :Mena Valley (2)... 57

    Figure 5-3 :Mena Valley (3)... 58Figure 5-4 :Arafat Area (1). 60

    Figure 5-5 :Arafat Valley (2) . 61

    Figure 5-6 : Arafat Area (3) 62Figure 6 -1 : The measured Noise level at King Abdul Aziz Street in

    Mina ( 13th of Dulhijja )67

    Figure 6 -2 : The measured Noise level at King Abdul Aziz Street in

    Mina ( 8thof Dulhijja ) 68

    Figure 6 -3 : The measured Noise level at King Abdul Aziz Street inMina ( 9thof Dulhijja )

    69

    Figure 6 -4 :The measured Noise level at King Abdul Aziz Street inMina ( 11thof Dulhijja )

    70

    Figure 6 -5 :The measured Noise level at King Abdul Aziz Street in

    Mina ( 12thof Dulhijja ) . 71Figure 6 -6 : The measured Noise level at King Abdul Aziz Street in

    Mina ( 13th of Dulhijja )72

    Figure 6 -7 : The maximum noise measured at various times at KingAbdulaziz Street in Mina.

    73

    Figure 6 -8 : The measured Noise level at King Abdulaziz Bridge in

    Mina ( 8th of Dulhijja ) 74

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    VIII

    LIST OF ILLUSTRATIONS(cont.) pageFigure 6 -9 : The measured Noise level at King Abdulaziz Bridge in

    Mina ( 9th of Dulhijja ) .

    75

    Figure 6 -10 : The measured Noise level at King Abdulaziz Bridgein Mina ( 10th of Dulhijja ) .

    76

    Figure 6 -11 : The measured Noise level at King Abdulaziz Bridge

    in Mina ( 11th of Dulhijja ) 77

    Figure 6 -12 : The measured Noise level at King Abdulaziz Bridge

    in Mina ( 12th of Dulhijja )78

    Figure 6 -13 :The maximum noise measured at various times at KingAbdulaziz Bridge in Mina.

    79

    Figure 6 -14 : The measured Noise level at Jamarat Ground Bridge

    in Mina (Jamrat Al-aqaba) 80Figure 6 -15 : The measured Noise level at Jamarat Ground Bridge

    in Mina (Al- Jamrah Al-Wasta)..81

    Figure 6 -16 : The measured Noise level at Jamarat Ground Bridgein Mina (Al- Jamrah Al-sughra ).

    82

    Figure 6 -17 : The measured Noise level at Jamarat Ground Bridgein Mina (Jamrat Al-aqaba)

    83

    Figure 6 -18 : The maximum Noise measured at various times atJamarat Ground Bridge in Mina ..

    84

    Figure 6 -19 : The measured Noise level at Jamarat Bridge, FirstFloor (Jamrat Al-aqaba). 85

    Figure 6 -20 : The measured Noise level at Jamarat Bridge, FirstFloor (Al- Jamrah Al-Wasta).

    86

    Figure 6 -21 : The measured Noise level at Jamarat Bridge, First

    Floor (Al- Jamrah Al-sughra )...87

    Figure 6 -22 : The measured Noise level at Jamarat Bridge, First

    Floor (Jamrah Al-Aqaba )..88

    Figure 6 -23 : The maximum Noise measured at various times atJamarat Bridge , First Floor in Mina .

    89

    Figure 6 -24 : The measured Noise level at Alkhaif mosque in Mina( 8th of Dulhijja ) .

    90

    Figure 6 -25 : The measured Noise level at Alkhaif mosque in Mina( 9th of Dulhijja ) .

    91

    Figure 6 -26 : The measured Noise level at Alkhaif mosque in Mina( 10th of Dulhijja ) ...

    92

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    IX

    LIST OF ILLUSTRATIONS(cont.) pageFigure 6 -23 : The maximum Noise measured at various times at

    Alkhaif Mosque in Mina .93

    Figure 6 -27 : The measured Noise level at AL-Rahmah Hospital inArafah ( 9th of Dulhijja ).

    94

    Figure 6 -28 : The measured Noise level at AL-Rafah Mountain inArafah( 9thof Dulhijja ) ..

    95

    Figure 6 -29 : measured The Noise level at Namerah Hospital inArafah ( 9th of Dulhijja ).

    96

    Figure 6 -30 : The measured Noise level at Namerah Mosque inArafah( 9th of Dulhijja )..

    97

    Figure 6 -31 :The measured Noise level at Road 4 (9th of Dulhijja) 98

    Figure 6 -32 : The measured Noise level at pedstrain( 9th of Dulhijja ).

    99

    Figure 6 -33 : The measured Noise level at Road No 8

    ( 9th of Dulhijja)...........................................................100

    Figure 6 -34 : The measured Noise level at Taradodiah

    (9th of Dulhijja)101

    Figure 6 -35 : The maximum Noise at various location in same time

    in Arafat Area1...102

    Figure 6 -36 : The maximum Noise at various location in same time

    in Arafat Area2.103

    Figure 6 -37 : Noise levels at different hearing frequencies for

    Motorcycle ..104

    Figure 6 -39 : Noise levels at different hearing frequencies for Civil

    Defense car alarm (1) 105

    Figure 6 -40 : Noise levels at different hearing frequencies for Civil

    Defense car alarm (2) ..106

    Figure 6 -41 : Noise levels at different hearing frequencies for Fan

    of tunnel...107

    Figure 6 -42 : Noise levels at different hearing frequencies for Car. 108

    Figure 6 -43 : Noise levels at different hearing frequencies for Bus. 109Figure 6 -44 : Noise levels at different hearing frequencies for

    Ambulance..110

    Figure 6 -45 : Noise levels at different hearing frequencies for

    Truck of Water..111

    Figure 6 -46 : Noise levels at different hearing frequencies for all

    Sources.112

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    X

    LIST OF TABLES

    Table PageTable 4- 1: The maximum time over which measurements can be made. 49

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    XI

    LIST OF SYMBOLS AND TECHNICAL TEARMS

    Broadband : Noise Measurements using parameters which include allthe audible noise, such as dB (A) and dB (C).

    Decibel (dB) : The units of sound level and noise exposuremeasurement.

    Leq : Equivalent continuous sound pressure level. A measureof the average sound pressure level during a period of

    time, t in dB.

    Peak : The maximum value reached by the Sound pressure atany instant during a measurement period in dB usually

    with C frequency weighting.

    SEL : Sound Exposure Level, displayed as LAE, LCEor LZE .

    SPL : Sound Pressure Level, the basic measure of noiseloudness, expressed in decibel.

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    Chapter 1

    Introduction

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    Chapter 1 Introduction

    - 2 -

    1 Introduction

    1.1Background

    The word "noise" is derived from the Latin word "nausea" meaning

    seasickness. Noise, defined as unwanted or excessive sound, is an

    undesirable by-product of our modern way of life. We experience noise in a

    number of ways. On some occasions, we can be both the cause and the

    victim of noise, such as when we are operating noisy appliances or

    equipment. There are also instances when we experience noise generated by

    others just as people experience second-hand smoke. While in both

    instances, noises are equally damaging. Second-hand noise is more

    troubling because it has negative impacts on us but is put into the

    environment by others, without our consent. The air into which second-

    hand noise is emitted and on which it travels is commons, for all people . It

    belongs to no one person or group, but to everyone. People, businesses, and

    organizations, therefore, do not have unlimited rights to broadcast noise as

    they please, as if the effects of noise were limited only to their private

    property. On the contrary, they have an obligation to use the commons in

    ways that are compatible with or do not detract from other uses. People,

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    Chapter 1 Introduction

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    businesses, and organizations that disregard the obligation to not interfere

    with others' use and enjoyment of the commons by producing noise

    pollution are, in many ways, acting like a bully in a school yard.

    There are two types of noise:

    (1) Steady: Continuous noise of sudden or gradual onset and long

    duration (more than 1 second). Examples: aircraft power plant noise,

    propeller noise, and pressurization system noise. According to the

    Occupational Safety and Health Administration (OSHA)[1], the maximum

    permissible continuous exposure level to steady noise in a working

    environment is 90 dB for 8 hours.

    (2) Impulse/blast: Noise pulses of sudden onset and brief duration

    (less than 1 second) that usually exceed an intensity of 140 dB . Examples:

    firing a handgun, detonating a firecracker, backfiring of a piston engine,

    high-volume squelching of radio equipment, and a sonic boom caused by

    breaking the sound barrier. The eardrum may be ruptured by intense levels

    (140dB) of impulse/blast noise. It is not a global problem because sound

    energy is not accumulated and the area, which suffers from noise, is limited

    to that around the noise source. In contrast, to many other environmental

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    Chapter 1 Introduction

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    problems, noise pollution continues to grow. This growth is unsustainable

    because it involves direct, as well as cumulative adverse health effects.

    In World Health Organization (WHO)[2] statements, "large city

    noise is considered to be the third most hazardous pollution". Researches

    study noise problems in cities and try to find a solution for these problem .

    At the time air pollution incurs a large bill to pay when it comes to stop the

    escalation of global warming, urban noise pollution is in fact another

    complex issue for which the academic community does not see possible

    short term plans to save the situation. It is only long term strategic planning

    that might realize some recovery to the current increasing levels of noise.

    However, transportation works is seen to be expanded and accelerated in

    terms of amount and variety (Berglund et aI., 2000; Kihlman, 2001); it is

    impractical to hinder traffic in main arterials or decrease traffic flow but it

    might be possible to detour traffic or to construct new roads, or other forms

    of end-of-pipe solutions. Noise will be a larger and serious social problem

    in the future if effective precautions are not taken accordingly.

    1.2The Importance of Study

    The first sanctuary appointed for mankind was that in Makkah , a

    blessed place , a guidance to the peoples , wherein are plain memorials ( of

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    Chapter 1 Introduction

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    Allah ' s guidance ) , the place where Abraham stood up to pray , and

    whosoever entered it is safe . A pilgrimage to the Holy Mosque in Makkah

    is a duty of Allah on all Muslim . At this Holy Sanctuary, Abraham have

    settled some of his posterity and called upon Mighty Cod :- ( Our Lord ! I

    have settle some of my posterity in an uncultivated valley(the valley of

    Makkah) near unto The Holy House, our Lord ! that they may establish

    proper worship ; so incline some hearts of men that they may yearn toward

    them , and provide Thou them with fruits in order that they may be thankful

    " The one God " Allah , the Beneficent , the Merciful ' granted Abraham's

    request : " And (remember) when We prepared for Abraham the place of

    the (holy) House , saying : Ascribe thou no thing as partner unto Me , and

    purify My House for those who make the round (thereof) and those who

    stand and those who bow and make prostration, proclaim unto mankind the

    pilgrimage, they will come unto thee on foot and on every lean camel ; they

    will come from every deep revine . That they may witness things that are of

    benefit to them , and mention the name of Allah on appointed days over the

    beast of cattle that He hath bestowed upon them. Then eat thereof and feed

    therewith the poor unfortunate. Then let them make an end of their

    unkemptness and their vows and go around the ancient House). The

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    Chapter 1 Introduction

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    pilgrimage is therefore an ancient pre- islamic rite , believed to be

    associated with man's first steps on earth . It takes place atArafat ,

    Muzdalifah , Mina valley and Makkah; and only once a year on the month

    of the lunar Dhul-hijjah , the twelfth month of the Muslim calendar

    .However aretian paganism has completely refrained the Hajj from its

    monotheistic message and spiritual objectives until the time of

    'Muhammad" the last Messenger of Allah and a Prophet of Islam " Allah

    peace and pleasing be upon him ". It is then when the Hajj was restored to

    its original form and became the fifth and final ethical principle or pillar of

    Islam as commanded by the Lord of the Worlds : " Now fulfill ye the Hajj

    and Umra to Allah " Moreover , the Prophet " Allah peace and pleasing be

    upon him " stated : " Those who perform the Hajj in the right manner and

    with full spiritual and emotional involvement shell come down from Arafat

    pure-as the day his mother gave birth to him". As such , the Hajj -to every

    Muslim- is therefore a declaration of Belief ,a process of renovation and

    expression of inspiration , motivation and devotion .No wonder , then , that

    Muslims from everywhere in the world dream of performing the Hajj at

    least once in their lifetime . It has recently become a well known fact that

    the number of pilgrims is increasing every year . This is due to the

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    increasing number of Muslims , particularly of Mo'omens (believers) who

    could afford the expenses and bear the efforts in volved in Hajj , and also

    because of the recent fast-mean facilities of transportation. The influx of

    these guests of Allah " the All-Merciful " imposes enormous responsibilities

    on the hosting country, the Kingdom of Saudi Arabia . Such responsibilities

    include the provision of the basic living needs and services for these

    heterogeneous guests and , above all , of the spiritual environment required

    for properly worshipping the all mighty God . The Saudi Arabian

    authorities , and in particular The Custodian of the Two Holy Mosques,

    Institute of Hajj Research are not withholding any possible effort necessary

    to preserve the spiritual environment and the fundamental principles of the

    Hajj. It deals with the quality of the atmospheric environment at Mina

    during the Hajj period , where pilgrims have to stay for at least three

    consecutive days. If not adequately conserved , such vital environmental

    factor could. badly affect their well-being and spiritual enjoyment of

    adoration and deep religious experience.

    1.3Objectives of Study

    Nowadays, the concern about the acoustic pollution is acquiring

    considerable importance. Studies about acoustic levels must be carried out

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    Chapter 1 Introduction

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    and unnecessary noise emissions are assigning to determine the noise map.

    Unlike other kinds of pollution the characteristics of noise contamination

    are not the same all over the world. These depend on such factors as the

    degree of development, the kind of activities involved, the population

    density, increasing number of vehicles, and even local habits and culture,

    etc. The noise pollution is importance as a stressing and possibly even

    dangerous affecting human life. Therefore this study aims to measure the

    noise levels at same site within the Holy Places during hajj period. The

    purpose is to provide information on the level of noise in order to identify

    sources of noise pollution.

    1.4The outlines of the study

    This study was subdivided to seven chapters those cover the whole

    project here .

    1.4.1Chapter 2: Physics of sound

    This chapter talks about human ear and how humans hear is a

    complex subject involving the fields of physiology, psychology and

    acoustics. It also discuss the Frequency Response Curves and basic Physics

    of sound .

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    Chapter 1 Introduction

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    1.4.2Chapter 3: Literature review

    There are several previous studies in the same topic and different

    countries of the world . We have mention some in this part.

    1.4.3Chapter 4: Instrumentation

    Noise measurements were performed using an integrated Average

    Sound Level Meter , model NO. CR812B, that developed by the Lirrus

    research PLC, in UK . After Hajj season, The Custodian of The Tow Holy

    Mosque Institute has obtained a developed high performance device

    carrying model NO. CR832B from the same company .

    1.4.4Chapter 5: Scope of work

    In this part the approach and style of the research have been

    illustrated from the beginning to the end .The chosen locations of

    measurements in Mina and Arafat regions have also been marked out.

    1.4.5Chapter 6: Result and discussion

    In this part of study some calculations on the data have made . Then,

    they were drawn in graphs and discussed for all regions of measurement .

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    1.4.6Chapter 7: Conclusion and recommendations

    In this part the research is summarized and the deducted results are

    written in addition to some proposed recommendations .

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    Chapter 2

    Physics of Sound

    and Human Ear

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    2 Physics of Sound and Human Ear

    2.1The Human Ear :

    Understanding how humans hear is a complex subject involving the

    fields of physiology, psychology and acoustics. We will attempt to

    understand how the human ear serves as an astounding transducer,

    converting sound energy to mechanical energy to a nerve impulse which is

    transmitted to the brain . The ear's ability to do this allows us to perceive

    the pitch of sounds by detection of the wave's frequencies, the loudness of

    sound by detection of the wave's amplitude and the timbre of the sound by

    the detection of the various frequencies which make up a complex sound

    wave.

    The ear consists of three basic parts ( see Figure 2-1 ) , the outer ear,

    the middle ear, and the inner ear. Each part of the ear serves a specific

    purpose in the task of detecting and interpreting sound. The outer ear serves

    to collect and channel sound to the middle ear. The middle ear serves to

    transform the energy of a sound wave into the internal vibrations of the

    bone structure of the middle ear and ultimately transform these vibrations

    into a compressional wave in the inner ear. The inner ear serves to

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    transform the energy of a compressional wave within the inner ear fluid into

    nerve impulses which can be transmitted to the brain. The three parts of the

    ear are shown in ( Figure 2-1 ).

    Figure 2-1 :The Human Ear. ( Source : Thomasom 2003Brooks/ cole. Fig. 14.27- page 452 )

    The outer ear consists of an ear flap and an approximately 2-cm long

    ear canal. The ear flap provides protection for the middle ear in order to

    prevent damage to the eardrum. The outer ear also channels sound waves,

    which reach the ear through the ear canal to the eardrum of the middle ear.

    Because of the length of the ear canal, it is capable of amplifying sounds

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    with frequencies of approximately 3000 Hz. As sound travels through the

    outer ear, the sound is still in the form of a pressure wave, with an

    alternating pattern of high and low pressure regions. It is not until the sound

    reaches the eardrum at the interface of the outer and the middle ear that the

    energy of the mechanical wave becomes converted into vibrations of the

    inner bone structure of the ear.

    The middle ear is an air-filled cavity which consists of an eardrum

    and three tiny, interconnected bones - the hammer, anvil, and stirrup. The

    eardrum is a very durable and tightly stretched membrane which vibrates as

    the incoming pressure waves reach it. As shown at the right, a compression

    forces the eardrum inward and a rarefaction forces the eardrum outward,

    thus vibrating the eardrum at the same frequency of the sound wave. Being

    connected to the hammer, the movements of the eardrum will set the

    hammer, anvil, and stirrup into motion at the same frequency of the sound

    wave. The stirrup is connected to the inner ear; and thus the vibrations of

    the stirrup are transmitted to the fluid of the middle ear and create a

    compression wave within the fluid. The three tiny bones of the middle ear

    act as levers to amplify the vibrations of the sound wave. Due to a

    mechanical advantage, the displacements of the stirrup are greater than that

    http://www.glenbrook.k12.il.us/GBSSCI/PHYS/Class/sound/u11l1c.htmlhttp://www.glenbrook.k12.il.us/GBSSCI/PHYS/Class/sound/u11l2a.htmlhttp://www.glenbrook.k12.il.us/GBSSCI/PHYS/Class/sound/u11l2a.htmlhttp://www.glenbrook.k12.il.us/GBSSCI/PHYS/Class/sound/u11l1c.html
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    of the hammer. Furthermore, since the pressure wave striking the large area

    of the eardrum is concentrated into the smaller area of the stirrup, the force

    of the vibrating stirrup is nearly 15 times larger than that of the eardrum.

    This feature enhances our ability of hear the faintest of sounds. The middle

    ear is an air-filled cavity which is connected by the Eustachian tube to the

    mouth. This connection allows for the equalization of pressure within the

    air-filled cavities of the ear. When this tube becomes clogged during a cold,

    the ear cavity is unable to equalize its pressure ; this will often lead to

    earaches and other pains.

    The inner ear consists of a cochlea, the semicircular canals, and the

    auditory nerve. The cochlea and the semicircular canals are filled with a

    water-like fluid. The fluid and nerve cells of the semicircular canals provide

    no roll in the task of hearing; they merely serve as accelerometers for

    detecting accelerated movements and assisting in the task of maintaining

    balance. The cochlea is a snail-shaped organ which would stretch to

    approximately 3 cm. In addition to being filled with fluid, the inner surface

    of the cochlea is lined with over 20 000 hair-like nerve cells which perform

    one of the most critical roles in our ability to hear. These nerve cells have a

    differ in length by minuscule amounts. They also have different degrees of

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    resiliency to the fluid which passes over them. As a compressional wave

    moves from the interface between the hammer of the middle ear and the

    oval window of the inner ear through the cochlea, the small hair-like nerve

    cells will be set in motion. Each hair cell has a natural sensitivity to a

    particular frequency of vibration. When the frequency of the compressional

    wave matches the natural frequency of the nerve cell, that nerve cell will

    resonate with a larger amplitude of vibration. This increased vibrational

    amplitude induces the cell to release an electrical impulse which passes

    along the auditory nerve towards the brain. In a process which is not clearly

    understood, the brain is capable of interpreting the qualities of the sound

    upon reception of these electric nerve impulses.

    2.2Frequency Response Curves :

    Frequency Response Curves are shown in Figures (2-2). Bottom

    curve is the threshold of hearing .Threshold of hearing is strongly

    dependent on frequency, Easiest frequency to hear is about 3000 Hz . When

    the sound is loud (top curve, threshold of pain) all frequencies can be heard

    equally .

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    2.3Physics of sound :

    2.3.1Sound :

    Sound is a vibratory disturbance created by a moving or vibrating

    source, in the pressure and density of a gaseous, liquid medium or in the

    elastic strain of a solid which is capable of being detected by the hearing

    organs. Sound may be thought of as mechanical energy of a vibrating object

    Figure 2-2 :Frequency Response Curve. ( Source : Fletcher and Munson,j.Acoust. Soc .Am., 1933 )

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    transmitted by pressure waves through a medium to human (or animal) ears.

    The medium of main concern is air.

    2.3.2Noise :

    Noise

    is defined sound that is loud, unpleasant, unexpected or

    undesired, and may therefore be classified as a more specific group of

    sounds. Perceptions of sound and noise are highly subjective: one person's

    music is another's headache. The two terms are often used synonymously,

    although few would call the sound that emanates from a highway anything

    but noise. Sound (and noise) is actually a process that consists of three

    components:

    1) The sound source.

    2) The sound path.

    3) The sound receiver.

    All three components must be present for sound to exist. Without a

    source to produce sound, there obviously is no sound. Likewise, without a

    medium to transmit sound pressure waves there is also no sound. Finally,

    sound must be received, i.e. a hearing organ, sensor, or object must be

    present to perceive, register, or be affected by sound or noise. In most

    situations, there are many different sound sources, paths, and receivers,

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    instead of just one of each. Acoustics

    is the field of science that deals with

    the production, propagation, reception, effects, and control of sound. The

    field is very broad, and transportation related noise and its abatement covers

    just a small, specialized part of acoustics.

    2.3.3Speed of Sound :

    When the surface of an object vibrates in air, it compresses a layer of

    air as the surface moves outward, and produces a rarefied zone as the

    surface moves inward. This results in a series of high and low air pressures

    waves (relative to the steady ambient atmospheric pressure) alternating in

    sympathy with the vibrations. These pressure waves - not the air itself -

    move away from the source at the speed of sound, or approximately 343

    m/s (1126 ft/sec) in air of 20 C. The speed of sound can be calculated from

    the following formula:

    PC 401.1 equ 1

    where :

    c = Speed of Sound at a given temperature, in meters per second (m/s).

    P = Air pressure in Newton per Square Meter (N/m2) or Pascals (Pa).

    = Air density in kilograms of mass per cubic meter (Kg/m3).

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    1.401 = the ratio of the specific heat of air under constant pressure to

    that of air in a constant volume.

    For a given air temperature and relative humidity, the ratio P/

    tends

    to remain constant in the atmosphere, because the density of air will reduce

    or increase proportionally with changes in pressure. Thus the speed of

    sound in our atmosphere is independent of air pressure. However, when air

    temperature changes, only changes, while P does not. The speed of sound

    is therefore temperature dependent, and also somewhat humidity dependent

    since humidity affects the density of air. The effects of the latter with

    regards to the speed of sound, however, can be ignored for our purposes.

    The fact that speed of sound changes with altitude, has nothing to do with

    the change in air pressure, and is only caused by the change in temperature.

    2.3.4Sound Characteristics :

    In its most basic form, a continuous sound can be described by its

    frequency

    or wavelength

    (pitch) and its amplitude

    (loudness).

    Frequency, Wavelength, Hertz :

    Wavelength() : The distance between crests of both curves of the

    sound.

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    Frequency (f) : The number of times per second that the wave passes

    from a period of compression through a period of

    rarefaction and starts another period of compression,

    it is expressed in cycles per second, or Hertz (Hz).

    Hertz (Hz): equals one cycle per second.

    High frequencies are sometimes more conveniently expressed in

    units of Kilo Hertz(KHz) or thousands of Hertz. The extreme range of

    frequencies that can be heard by the healthiest human ears spans from 16 to

    20 Hz on the low end to about 20000 Hz (or 20KHz) on the high end.

    Frequencies are heard as the pitch or tone of sound. High pitchedsounds

    produce high frequencies, low pitched sounds produce low frequencies.

    Very-low frequency airborne sound of sufficient amplitude may be felt

    before it can be heard, and is often confused with earthborn vibrations.

    Sound below 16 Hz is referred to as infrasound, while high frequency sound

    above 20000 Hz is called ultrasound. Both infra- and ultrasound are not

    audible to humans.

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    The distance traveled by a sound pressure wave through one

    complete cycle is referred to as the wavelength. The duration of one cycle is

    called the period. The period is the inverse of the frequency.

    The frequency

    of sound pressure waves increases, as their wavelength shortens, and vice

    versa. The relationship between frequency and wavelength is linked by the

    speed of sound, as shown in the following equations :

    FC equ. # 2

    CF equ. # 3

    FC equ. # 4

    Where :

    = Wavelength (nm or Ao).

    While nm= 10-9m and Ao =10-10m .

    c = Speed of Sound (343.3 m/s, or 1126.5 ft/sec at 20oC, or 68oF).

    Figure 2-3 : Spatial pressure distribution in a plane wave at one instant of time.

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    f = Frequency (Hertz).

    Although the speed of sound is usually thought of as a constant, we

    have already seen that it actually varies with temperature. The above

    mathematical relationships hold true for any value of the speed of sound.

    Frequency is normally generated by mechanical processes at the source, and

    is therefore not affected by air temperature. As a result, wavelength usually

    varies directly speed of sound as the latter varies with temperature. The

    relationships between frequency, wavelength and speed of sound can easily

    be visualized by using the analogy of a train traveling at a given constant

    speed.

    Sound Pressure Levels (SPL), Decibels (dB):

    The pressures of sound waves continuously changes with time or

    distance, and within certain ranges. The ranges of these pressure

    fluctuations (actually deviations from the ambient air pressure) are called

    the amplitude of the pressure waves. Whereas the frequency of the sound

    waves is responsible for the pitch or tone of a sound, the amplitude

    determines the loudness of the sound. Loudness of sound increases and

    decreases with the amplitude.

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    Sound pressures can be measured in units of micro Newtons per

    square meter (N/m2) called micro Pascals (Pa). 1 Pa is approximately

    one-hundred billionth of the normal atmospheric pressure. The pressure of a

    very loud sound may be 200,000,000 Pa, or 10,000,000 times the pressure

    of the weakest audible sound (20 Pa). Expressing sound levels in terms of

    Pa would be very cumbersome, because of this wide range. For this

    reason, sound pressure levels (SPL) are described in logarithmic units of

    ratios of actual sound pressures to a reference pressure squared.

    In its simplest form, sound pressure level in

    decibels is expressed by

    the term:

    Sound Pressure Level (SPL) = 10 Log10(0

    1

    P

    P )

    2 dB equ. 5

    Where:

    P1is sound pressure.

    P0is a reference pressure, standardized as 20 Pa.

    Noise Measurement

    The equivalent sound level Leq is the A-Weighted sound pressure

    level averaged over a suitable time period T . The averaging time T can be

    chosen to be a number of minutes , hours or days , as desired.

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    dBref

    PdtA

    PTLeq ]2/2)/1[(10

    log10 equ. 6

    where PA is the instantaneous sound pressure measured using an A-

    weighting frequency filter . The Leq is also sometimes known as the average

    sound level LAT.

    Leq calculation :

    The Leqdescriptor is a special sort of average noise level. Instead of

    averaging decibel levels, the energy levels are averaged. The Leq is also

    called an energy-mean noise level. The instant noise levels over a certain

    time period are energy-averaged by first converting all dB A values to

    relative energy values , these values are added up and the total is divided by

    the number of values. The result is average (relative) energy. The final step

    then is to convert the average energy value back to a decibel level. The

    below equation showed the method of adding the energy values. This

    equation can be expanded to yield an Leq:

    Leq=10log10[(10SPL(1)/10

    +10SPL(2)/10

    +10SPL(n)/10

    )/N] equ.7

    Where :

    N = number of noise level samples .

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    Chapter 3

    Literature Review

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    3 Literature Review

    This section include some of the scientific researches occurred in

    different places and countries around the world that related to our studying

    in the noise pollution.

    3.1The Studies :

    3.1.1Abu Dhabi, UAE : 1998 AD

    The name of this study is NOISE MODELLING STUDY

    TAWEELAH B EXTENSION PROJECT[3]

    This research was done by Parsons Brinckerhoff Ltd (PB) to make a

    noise modelling study of the Al-Taweelah power and desalination plants

    near Abu Dhabi, UAE July 1998.

    This assessment aims to model existing noise sources and to predict

    boundary noise levels before and after the proposed extension to verify

    compliance with the limits, and to provide the operator with a noise contour

    map of the site and adjoining land area.

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    3.1.2Isfahan urban areas: 2003 AD

    The name of this study is Evaluation of noise pollution in Isfahanz

    urban areas[4]:

    The sound levels have been sampled in fall and winter in2003. The

    samples were taken from most crowded areas.

    Methods:This research is based on the results of outdoor sound level

    measurements carried out in a total of 18 different urban locations in

    Isfahan city. The indices include values such as main percentiles (L1, L10,

    L50, L90), SEL, Leqand NPL.

    Results:The results showed that Max Leq was 74.4 dB(A). The level

    of SEL varied from 96.4 to 107.4 dB(A). The level of SEL was over 104

    dB(A) at some of the stations. It was also found that level of TNI varied

    from 60.6 to Max of 77.2 dB(A). This research done by : Suhela

    Murtathay,Bezen Bena and Nedam Adenn.

    3.1.3Makkah : 2003 AD

    The name of study is Determination noising levels in the small

    Market Tunnel[5].

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    This study was conducted to determine noising levels in the small

    Market Tunnel in MAKKAH

    DR-SHAHATAH Scored a lot of goals in his study by measuring the noise

    level in the tunnel, establishing an electronic map describing the noising

    levels, established a map of different activities inside the tunnel

    (distribution of people and their location). He indicated the subjected levels

    inside the tunnels by making a comparison between the two established

    maps. Finally he compared his results with the international and local

    standards. The readings were recorded during the 24,25,26 of Ramadan at

    an average of 1:30 hour for each day and the noise founded there is higher

    than the acceptable level.

    3.1.4London : 2004 AD

    The name of study is The London Road Traffic Noise Map [6]:

    Done by Department for Environment, Food and Rural Affairs. This

    report describes how the London Road Traffic Noise Map was created. The

    noise calculations covered an area of over 1,600 km2

    , the map contains

    about 16,575,000 calculation points. The method used in this report is the

    Calculation of Road Traffic Noise (CRTN). The project achieved its goal

    of producing a strategic road traffic noise map for the Greater London area.

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    The level of noise recorded in this study varies between acceptable and

    unacceptable noise.

    3.1.5Jordan : 2005 AD

    The name of study is Attitudes of Jordanian Population Towards

    Road Traffic Noise[7].

    This study was done by Ayman N. Al-Dakhlallaha* and Khair S.

    Jadaan in August 25, 2005 The purpose of this study is to quantify the

    levels of noise which are generated from road traffic and compare these

    measured levels against appropriate standards for noise of this type.

    Measurements of traffic noise were performed using a noise level meter

    type 4426.

    Measurement sites were located in Amman, and were chosen so as to

    provide as far as possible a comprehensive coverage over the urban area.

    The statistical analyzer used produced the result by hourly measures during

    the study period ( 6:00 to 12:00 midnight ).

    The study established that residential areas adjacent to the sites where

    traffic noise was measured are subjected to noise levels of up to 78 dB(A).

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    3.1.6England : 2007 AD

    Traffic Noise in England, wasdone by Deepak Prasher .Professor of

    Audiology in Ear Institute in the University College London[8]. This report

    describes the noise levels in 41 towns and cities in England measured

    during October and November 2006.A Bruel and Kjaer 2260 investigator

    system was used to record noise levels in streets around the towns and city

    centres.Some surprising results in the survey were identified. Some small

    towns showed higher levels of noise than expected such as Darlington,

    Doncaster and Gillingham appearing in the top 10 noisy places. The Tyne

    Bridge in Newcastleupon-Tyne was the number one noise spot exceeding

    the first action level of the noise at work regulations with levels exceeding

    80dB LAeq. Torquay was the quietest of the 41 places surveyed with a level

    of just over 60dB

    3.2Effect of noise :

    The perception of sounds in day-to-day life is a major importance for

    human well being. Communication through speech, sounds from playing

    children, music, and natural sounds in parklands, parks and gardens are all

    examples of sounds essential for satisfaction in every day life. According to

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    the International Program on Chemical Safety (WHO 1994)[1], an adverse

    effect of noise is defined as a change in the morphology and physiology of

    an organism that results in impairment of functional capacity, or an

    impairment of capacity to compensate for additional stress, or increases the

    susceptibility of an organism to the harmful effects of other environmental

    influences. This definition includes any temporary or long-term lowering of

    the physical, psychological or social functioning of humans or human

    organs. The health significance of noise pollution are: noise-induced

    hearing impairment; interference with speech communication; disturbance

    of rest and sleep; psycho physiological, mental-health and performance

    effects; effects on residential behavior and annoyance; as well as

    interference with intended activities [9]

    The specific effects of noise on individual human health are difficult

    to establish, mainly because individuals' sensitivity to noise is highly

    variable. However, recent studies[9-21]show that noise is a major source of

    stress, with physiological reactions including accelerated heart rhythm,

    increased amounts of hormones produced and dilation of the pupils. Noise

    also increases the stress already present from difficult social, familial or

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    professional relationships as well as the health problems and can intensify

    the development of mental disorder.

    Other general impacts of noise include:

    Hearing impairment can occur at noise level of 85 dB (A) ( so

    this is not the most important effect) [10, 11];

    Intelligibility of speech[12];

    Physiological effects, such as tiredness (from muscle

    contraction) and hypertension (from contraction of blood

    vessels) [13, 14].

    Sleep disturbance[15];

    Performance in cognitive tasks (from lack of concentration and

    precision in actions) [16, 17].

    Decrease of children's ability to comprehend, concentrate and

    assimilate. Young children in the process of acquiring

    language and reading skills are particularly at risk [18].

    Mental health problems [19].

    Noise from numerous sources will typically have some combination

    of effects; such as interfering with speech in the day and disturbing sleep at

    night. It is important to note that the effects of noise are often more severe

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    on vulnerable subgroups; such as the elderly, young children, blind people

    and people in hospitals or rehabilitating at home.

    The noise effects are very dependent on specific factors, such as the

    time duration, noise source level, and the distance from the source . The

    duration of a noise event, and its tone, can influence perceived annoyance.

    For example, an aircraft's tone is perceived as threatening (it integrates

    notions of fear) and is therefore typically more annoying than the same

    level (intensity and frequency) of train noise. Some types of tone are even

    considered relaxing (wave noise, bird song) and therefore cannot be treated

    as noise.

    Another specificity to take into account is what is called the

    emergence of a noise (the size of fluctuation from the background noise

    level). This characteristic is very important when considering night-time

    noise, as emergence is one of the most important causes of sleep disruption.

    This is in turn responsible for a series of severe health effects, which were

    acknowledged by the European Commission [20].

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    Chapter 4

    Instrumentation

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    4 Instrumentation

    4.1Sound Level Meter CR 812B :

    Noise measurements were performed using an integrated Average

    Sound Level Meter , model NO. CR812B, that developed by the Cirrus

    research PLC, in UK . After the Hajj season is over the Custodian Of The

    Tow Holy Mosque Institute has obtained a developed high performance

    device carrying model NO. CR832B from the same company .

    4.2Specifications :

    The weight of the instrument is : 450 gms

    Batteries : 2 X 1.5 v Alkaline LR6 / AA

    Dimensions : 340 mm X 75 mm X 25 mm

    Environmental :

    1 ) Temperature : Operating - 10 C to + 50 C

    Storage - 20 C to + 60 C

    2 ) Humidity : up to 95 % RH Non condensing .

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    4.3Measurement Functions:

    The Measurement functions depend upon the options that have been

    fitted. The instrument can be fitted with either Broad Band or the Octave

    Band modes. If the Auto Repeat function is used, it can be made to repeat

    the broad Band measurement up to 999 times. The instrument can also be

    configured to synchronise the measurement start time with the instrument

    clock.

    4.3.1 BroadBand Measurement Mode:

    In BroadBand Mode, the instrument store the overall values such as

    LAeq

    LAFmax

    and Lns as well as storing a noise profile, or Time History,

    during each measurement.

    The instrument can store up to 1300 BroadBand Measurements

    which can be of any length, up to a maximum of 99 hours per measurement.

    With each measurement is stored, a noise profile which consists of 1 second

    Leq samples, with up to a maximum of 11 days of noise profile being

    available.

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    4.3.2 Octave Band Measurement:

    The Instrument provide a sequential sweep through the filter bands

    over the measurement duration and provide a measurement of the overall

    LAeq, LCeqand LZeq functions , when the instrument is set either to 1:1 or 1:3

    Octave Band Mode, the Run Duration is divided between the frequency

    bands. For example, if the instrument duration is set to 15 minute the

    equipment will take a total of 15 minutes to complete the sweep through the

    frequency band.

    4.4 Sound Level Meter Calibration:

    IF the Sound Level Meter need to be used for measurement, the

    instrument must be calibrated against the Acoustic calibratior.

    Durring calibration connect the Acoustic Calibrator to the Sound

    Level Meter and select the 94 dB setting on the Acoustic Calibrator. Press

    the menu key to select the calibrate option and press OK to start the

    calibration procedure ( see figure 4-1).

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    The configuration of the Run Duration, the Auto-Repeat and the

    Auto-Synchronise function are all connected and affect each other and must

    be set before measurement.

    4.5The measurement duration:

    The measurement duration is set to the specific time interval and the

    instrument will run continuously until the stop key is pressed. In our study

    the measurement duration was 15 minutes until reach to the next point.

    Figure 4-1 : Noise the status of the different functions.

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    4.6The Measurement Auto-Repeat:

    The Auto- Repeat function is used to set the instrument to make a

    series of continuous measurement. If the measurement duration was set to

    15 minutes and the Auto Repeat disabled, after the first 15 minute

    measurement the instrument will stop and store the measurement

    information at the memory. With the Auto Repeat function enabled, the

    instrument will make further 15 minute measurements, one after the next

    until the total number of measurement has been made. This allows the user

    to set the instrument, for example, to take 96 individual 15 minute

    measurement over a 24 hour period.

    4.7The measurement Auto- Synchronise:

    This function allows the start of the measurement to be started in

    time with the clock of the instrument.

    The diagram below shows how the measurement runs from when the

    start key is pressed for the duration defined by the Run Duration (see figure

    4-2).

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    This method of starting and stopping the measurements is used in

    many applications such as Environmental Noise measurements, it is

    important to start the measurements at a predetermined time. For example,

    when making environmental noise measurements that are for 10 minutes,

    the equipment can start the measurements on 10 minute boundaries.

    4.8Measurement Range:

    One of the most important features of a Sound Level Meter is the

    measurement range. If the measurements rang is set too high, the instrument

    may not be able to record low level. If the measurement range is set too

    low, high noise levels will overload the instrument and make the

    measurement invalid. Therefore it is vital that the correct measurement rang

    is chosen for the noise to be recorded.

    Figure 4-2 : The Run Duration of the measurement defined.

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    The measurement range in our study is (50 dB to 120 dB), if the

    noise level is below 50 dB, the instrument will indicate under- Rang. If the

    noise level is above 120 dB, the instrument will indicate Overload.

    The bar graph at the top of the screen can be used to select the

    appropriate measurement rang. As the user moves between the different

    measurements ranges, the bar graph changes the top and bottom to match

    the measurement range. The noise level being measured is shown in the bar

    graph.

    4.9Windshield:

    The equipment used with UA: 237 90mm Foam Windshield which

    will reduce the noise levels generated by air turbulence over the

    microphone capsule (see figure 4-3). The windshield can also be protecting

    the microphone capsule of the Sound Level Meter from dust and fluids

    which may affect the performance of the instrument. The UA: 237

    windshields must be removed before the Sound Level Meter can be

    calibrated.

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    Figure 4 -3 :The Windshield Foam.

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    4.10 The Batteries:

    The batteries of the instrument are located behind the cover on the

    bottom of the instrument. It is use two AA type batteries, also known as

    LR6 ( see figure 4-4 ).

    1. Batteries.

    2. RS232 Communications Socket

    3. External power.

    Stopping and recalling the measurement:

    When the measurement is stopped, the data is automatically stored in

    the memory and the instrument enters the measurement review mode.

    Figure 4 -4 :The positions of the Batteries.

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    To view stored measurements, ensure that the instrument is not

    running and move the arrow up or down in the review mode to see the first

    and the last measurement.

    4.11 Sound Level Meter Configuration :

    The Keypad is shown in Figure 4-5 :

    1. Move through the measurement parameters when running a

    measurement, move through the stored measurement

    parameters in memory recall mode, select a higher frequency

    band Octave Band Filter mode and set up through menu

    option.

    Figure 4 -5 :The Keypad of the instrument.

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    2. Chang the measurement range and display the current

    measurement range.

    3. Enter the memory Recall mode and step through the memory

    locations.

    4. Move through the measurement parameters when running the

    measurement, move through the stored measurement

    parameters in memory recall mode, select a lower frequency

    band in Octave Band mode and step down through menu

    options.

    5. Resets the current measurement when running.

    6. Power On and Off.

    7. Stops the current measurement when running.

    8. Start and pause a measurement.

    9. Switch on and off the display backlight.

    10.Exit menu option. Cancel data entry.

    11.Select menu option. Accept data entry.

    12.Enter memory Recall Mode and step through the memory

    locations.

    13.Select the menu mode and view the menu options.

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    4.12 Menu System:

    The instruments use a menu system to allow the user to change the

    operation of the Sound Level Meter.

    This menu system is described below along with the procedure to

    change the different measurement functions and operational parameters.

    4.13 Viewing and downloading the measurement :

    Configuring the instrument from the software :

    Different configurations can be saved and loaded into the instrument

    to suit different measurement applications. The following parameters can be

    set from within the Deaf Defier3 software:

    Measurement mode.

    Run Duration.

    Time Weighting.

    Frequency Weighting.

    Measurement Rang.

    User Metric.

    Measurement Auto Synchronisation.

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    Measurement Auto Repeat.

    Ln values.

    Understanding how the measurements are stored :

    The memory of the instrument can store up to 1300 measurements.

    Each measurement is known as an Event and can be either BroadBand, 1:1

    Octave Band or 1: 3 Octave Band. The duration of each measurement does

    not affect the size that it takes, but the different measurements types take up

    different amounts of space in the instrument memory.

    Figure 4 -6 :The Deaf Defier3 software .

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    The diagram below shows how the different measurements take up

    different amounts of memory space ( figure 4-7 ).

    The maximum time over which BroadBand measurements can be

    stored depends upon the duration of the measurements.

    Table 1: The maximum time over which measurements can be made.

    Measurement DurationMaximum Length

    Measurement

    1 minute 21.5 hours

    5 minutes 4.5 days

    15 minutes 13.5 days

    30 minutes 27 days

    1 hour 54 days

    Figure 4 -7 :The space of the different measurements of the instrument.

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    When each BroadBand measurement is stored a Time History

    measurement, this information is stored in a separated memory from the

    Events and does not take up any of the 1300 Event memories However, the

    time history memory is limited to a size of 1008000 samples at 1 second

    samples, which is just over 11 days storage. If the Time History Store is full

    before the Event Memory Store, the Event measurements will continue but

    will not have Time History

    data. The diagram shows an example of this, in (figure 4-8 ).

    Figure 4-8 :The space of the different measurements of the instrument.

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    4.14 Maintenance and Care

    The instrument is precision measurement and should be treated withcare:

    1. The instrument should not be exposed to substances which

    may cause damage to the components of the unit.

    2. If the instrument is to be used in an environment where

    particles such as dust may come into contact with the

    instrument, always use a windshield to protect the microphone

    capsule.

    3. The instrument is not waterproof and should not be used in

    situations where will form or condense on the microphone

    capsule or the instrument body.

    4. If using the CR: 812B outdoor, use a suitable outdoor

    measurement kit which has been specifically designed to

    protect the instrument.

    5. If the CR: 812B becomes dusty, wipe it down with a cloth that

    is lightly dampened with water or a mild detergent.

    6. The aromatic hydrocarbons, chlorinated solvents, or methanol-

    based fluids should not be using when wiping down the meter.

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    7. The microphone capsule should not be cleaned and the

    microphone grill should not be removed as this can cause

    severe damage to the membrane.

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    Chapter 5

    Scope of Work

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    5 Scope of Work

    The project is thoroughly studied to know its importance and benefit .

    Making the necessary equipment to make the study available and

    training those who are taking part in measurement how to use the

    device .

    Choosing measurement locations : This should be according to the

    places where pilgrims are concentrated at a specific time. Also

    according to vital places such as hospitals and intersections of main

    roads .

    The places were chosen as follows :

    5.1Mina Valley :

    5.1.1 King Fahad street :

    One of the main roads in Mina .The measurement point was chosen

    near King Fahad Tunnel as shown in Figure (4-1), point No ( 1 ) at

    longitude and latitude ( 21 25' 29.50" N , 39 52' 14.22" E).

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    5.1.2King Abdulaziz Street :

    King Abdulaziz Street is the main street in Mina valley. The selected

    points of measurement in front of the Civil Defense building on the

    opposite side of road as shown in Figure (5-1), point No ( 2 ) at longitude

    and latitude ( 21 25' 11.85" N , 39 52' 11.56" E).

    5.1.3Al-Jamarat Bridge :

    The measurement location was chosen next to Al- Jamarat where the

    measurement was taken at a distance of 35 meters away from Al- Jamarat

    basin as shown in Figure (5-1).

    The first day is Eid Al-Adha (10/12/1427) ( 30/12/2006) : Jamrat Al-

    Aqaba point No ( 3 ) at longitude and latitude( 21 25' 18.79" N ,

    39 52' 15.25" E).

    First day of Tashreeq (11/12/1427) ( 31/12/2006) : Al-jamrah Al-

    sughra , point No ( 4 ) at longitude and latitude ( 21 25' 16.02" N ,

    39 52' 21.00" E).

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    Second day of Tashreeq : (12/12/1427) ( 1/1/2007) : Al- Jamrah Al-

    Wasta point No ( 5 ) at longitude and latitude ( 21 25' 12.66" N , 39

    52' 26.77" E).

    Third day of Tshreeq : (10/12/1427)( 30/12/2007): Jamrat Al-Aqaba.

    Figure 5-1 :Mina Valley (1).

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    5.1.4 King Abdulaziz Bridge :

    The measurement point was chosen at the intersection of King Abdul

    Aziz Road and King Abdullah Road near Mina Bridge Hospital as shown in

    Figure (5-2), point No ( 6 ) at longitude and latitude ( 21 24' 21.35" N , 39

    53' 20.84" E).

    Figure 5-2 :Mina Valley (2).

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    5.1.5Al-Kheef Mosque :

    In front of the mosque there is a large plaza considered as a main

    pedestrian way connecting Al-Jamarat with the rest of Mina 3 locations for

    measurement were chosen in front of the mosque at one houre as shown in

    Figure (5-3).

    Figure 5-3 :Mina Valley (3).

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    Point ( 7 ) at longitude and latitude ( 21 24' 57.54" N , 39 52'

    43.14" E).

    Point ( 8 ) at longitude and latitude ( 21 24' 59.14" N , 39 52'

    40.55" E).

    Point ( 9 ) at longitude and latitude ( 21 25' 00.50" N , 39 52'

    39.47" E).

    5.2Arafat Area :

    5.2.1Namirah Hospital :

    The point was chosen as shown in Figure (5-4), point No ( 1 ) at

    longitude and latitude ( 21 21' 11.48" N , 39 58' 23.13" E).

    5.2.2Namerah Mosque :

    A main landmark in Arafat . Pilgrims pray Noon (Zuhr) and

    Afternoon (Assr) prayers shortened and combined. The measurement point

    was chosen as shown in Figurer (5-4), point number ( 2 ) at longitude and

    latitude ( 21 21' 10.47" N , 39 58' 22.29" E).

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    5.2.3Al-Rahmah Mountain :

    A main landmark in Arafat . Masses of pilgrims stand on it. The

    measurement point was chosen as shown in Figurer (5-4), point

    number ( 3 ) at longitude and latitude ( 21 21' 14.00" N , 39 59' 02.30" E).

    5.2.4Al-Rahmah Hospital :

    Al-Rahmah hospital is located anear Al-Rahmah mountain. The

    measurement point was chosen as shown in Figurer (5-4), point number (4)

    at longitude and latitude ( 21 21' 11.74" N , 39 58' 58.6" E).

    Figure 5-4 :Arafat Area (1).

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    5.2.5Pedestrian Way :

    The location was chosen at the end of Arafat from the side of

    Muzdalifa as shown in Figurer (5-5), point number ( 5 ) at longitude and

    latitude ( 21 21' 19.91" N , 39 57' 55.17" E).

    5.2.6Road NO. 4 :

    The measurement point was chosen as shown in Figurer (5-5), point

    number ( 6 ) at longitude and latitude ( 21 21' 09.98" N , 39 57' 28.62" E).

    Figure 5-5 :Arafat Valley (2).

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    5.2.7Road NO. 8 :

    The measurement point was chosen as shown in Figurer (5-6), point

    number ( 7 ) at longitude and latitude ( 21 21' 44.39" N , 39 58' 38.00" E).

    5.2.8Taradodiah :

    The measurement point was chosen as shown in Figurer (5-6), point

    number ( 8 ) at longitude and latitude ( 21 22' 33.66" N , 39 58' 52.46" E).

    Figure 5-6 : Arafat Area (3) .

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    Chapter 6

    Results and

    Discussion

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    6 Results and Discussion

    6.1 Some Hajj Rites :

    We are going to mention here some Hajj rites performed by pilgrims

    in order to know the places where they concentrate in those days ( at the

    time of the study ).

    The 8thof Dulhijja (Tarwiah Day) :

    The Hajj rites start in this day where the most of pilgrims move to

    their camps in Mina before afternoon. In Mina, the pilgrims pray Dhuhr,

    Asr, Maghrib and Ishaa of the 8 thof Dhul-Hijjah and Fajr of the 9thof Dhul-

    Hijja (Arafat Day). The most essential hajj rites start in the early morning of

    the 9thday of the month of Dulhijja, when pilgrims descend to the Arafat

    area.

    The 9thof Dulhijja (day of Arafat) :

    In the 9th of Dulhijja (day of Arafat) pilgrims accumulate in

    AL-Rahmah Mountain and Namrah Mosque . The pilgrims descend after

    sunset to mzdalefh .

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    The 10thof Dulhijja (day of al-Nahr) :

    In this great day all the pilgrims throw only the biggest jamrah (al-

    kabah) after the sunrise until the sunset (Zawal time), scarifying the cheep

    and cut their hair.

    The 11thof Dulhijja (The First day of Tashriq days) :

    In this day the pilgrims must stay most of the night in Mina .Then

    after the zawal time (Zuhur prayer time) of the first Tashriq day, the

    pilgrims go to throw seven (7) pebbles at each of the three (3) jamrah

    stations.

    The 12thof Dulhijja (The second day of Tashriq days ) :

    On the second day of the Tashriq days, the pilgrims again throw

    pebbles at the three jamrahrat, as the previous day. If they stay in Mina until

    the sun sets on the second day, it becomes an obligation upon them to stay

    the last night of Tashreeq days and throw the pebbles at the jamarat on the

    third Tashreeq day.

    The 13thof Dulhijja (The third day of Tashriq days) :

    After the zawal time of the third Tashriq day, the pilgrims go to

    throw seven (7) pebbles at each of the three (3) jamarat stations.

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    6.2 Calculation :

    The measurement was reported in 15 min and we convert it in 1

    hour by using the equation :

    Leq = 10 log 10{[ 10(SPL/10)

    (1)++10(SPL/10)

    (n) /n]} equ. 8

    The WHO, 1999, was reported that if the measurements were greater

    than Leq = 85 db per hour will causes hearing impairment.

    6.3 Mina Valley :

    6.3.1 King fahad Street:

    King Fahad Street is the main street in mina valley . The selected

    point of measurement is after King fahad tunnel . The selected location is

    shown in Figure (5-1) at point number ( 1 ).

    The 8thof Dulhijja (Tarwiah Day)( 28/12/2006):

    The variation level of noise are shown in Figure (6-1). Readings were taken

    between 02:00 and 22:00.

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    The maximum level of noise is (Leq = 76.54dB per hour) at 11:00.

    The Leq = 76.54 dB is less than Leq = 85 dB so that, this area is suitable for

    human hearing.

    6.3.2 King Abdulaziz Street:

    King Abdulaziz Street is the main street in mina valley . The selected

    points of measurement in front of the Civil Defense building on the

    60

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    85

    90

    95

    100

    2 3 4 5 6 7 8 9 101112131415161718192021

    Time (Hour )EquivalentContinuo

    sSound

    Level(dB)

    Figure 6 -1 :The Measured Noise level at King fahad Street in Mina ( 8t

    of Dulhijja ) .

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    opposite side of road. The selected location is shown in Figure (5-1) at

    point number ( 2 ).

    The 8thof Dulhijja (Tarwiah Day)( 28/12/2006):

    The variation level of noise are shown in Figures (6-2). Readings

    were taken between 02:00 and 22:00.

    The maximum level of noise is (Leq = 75 dB) at 20:00. The Leq =

    75 dB is less than Leq = 85 dB so that, this area is suitable for human

    hearing.

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    95

    100

    01 02 03 04 05 06 07 08 09 10 11 12 13 14 15 16 17 18 19 20 21

    Time (Hour )

    EquivalentC

    ontinuosSound

    Level(dB)

    Figure 6 -2 : The measured Noise level at King Abdul Aziz Street in Mina ( 8th

    of Dulhijja ) .

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    The 9thof Dulhijja (day of Arafat)( 29/12/2006):

    The variation levels of noise are shown in Figure (6-3). Readings

    were taken between 07:00 and 10:30.

    The maximum level of noise is (Leq = 78.34 dB) at 07:00.

    The Leq = 78.34 dB is less than Leq = 85 dB so that, this area is suitable for

    human hearing.

    Figure 6 -3 : The measured Noise level at King Abdul Aziz Street in Mina ( 9th

    of Dulhijja ) .

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    The 11thof Dulhijja (The first day of Tashriq days)

    ( 31/12/2006):

    The variation levels of noise are shown in Figure (6-4). Readings

    were taken between 10:00 and 00:00.

    The maximum level of noise is (Leq = 85.04 dB) at 22:00.

    The Leq = 85.04 dB is approximately equal to Leq = 85 dB, so that, this

    area is still within the recommended noise value by WHO 1999.

    Figure 6 -4 :The measured Noise level at King Abdul Aziz Street in Mina ( 11th

    of Dulhijja ) .

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    The 12thof Dulhijja (The second of Tashriq days )

    ( 01/01/2007) :

    The variation levels of noise are shown in Figure (6-5). Readings

    were taken between 10:00 and 21:00 .

    The maximum level of noise is (Leq = 78.39 dB) at 20:00.

    The Leq = 78.39 dB is less than Leq = 85 dB so that, this area is suitable for

    human hearing.

    Figure 6 -5 :The measured Noise level at King Abdul Aziz Street in Mina ( 12th

    of Dulhijja ) .

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    The 13thof Dulhijja (The third of Tashriq days)

    ( 02.01/2007):

    The variation levels of noise are shown in Figure (6-6). Readings

    were taken between 10:00 and 17:00.

    The maximum level of noise is (Leq = 78.26 ) dB at 16:00 .

    The Leq = 78.26 dB is less than Leq = 85 dB so that, this area is suitable for

    human hearing.

    Figure 6 -6 : The measured Noise level at King Abdul Aziz Street in Mina ( 13th

    of Dulhijja ) .

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    130140

    8th of

    Dulhijja

    9th of

    Dulhijja

    11th of

    Dulhijja

    12th of

    Dulhijja

    13th of

    Dulhijja

    Time ( Day )

    Sound

    Level(dB)

    Highest of Leq

    Highest LMax

    Highest Peak

    Over View of Level Noise in King Abdul Aziz Street:

    The variation level of noise at various time are shown in

    Figure (6-7).

    It can be noted from the figure that noise level in most time is

    acceptable . The 11thday has the highest level of noise in this location .The

    maximum meured was = 80 dB in The 11th of Dulhijja see the figure

    above.

    Figure 6 -7 : The maximum noise measured at various times at King Abdulaziz Street in Mina.

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    6.3.3 King Abdulaziz Bridge :

    King Abdulaziz Street is the main street in mina valley . The selected

    points of measurement at the intersection of King Abdulaziz Road and King

    Abdullah Road near Mina Bridge Hospital The selected location is shown

    in Figure (5-2) at point number ( 6 ).

    The 8thof Dulhijja (Tarwiah Day)( 28/12/2006):

    The variation level of noise are shown in Figures (6-8). Readings

    were taken between 09:00 and 21:00.

    Figure 6 -8 :The measured Noise level at King Abdulaziz Bridge in Mina ( 8th

    of Dulhijja ) .

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    The maximum level of noise is (Leq = 75.00dB) at 20:00.

    The Leq = 75.00 dB is less than Leq = 85 dB so that, this area is suitable for

    human hearing.

    The 9thof Dulhijja (day of Arafat)( 29/12/2006):

    The variation levels of noise are shown in Figure (6-9). Readings

    were taken between 08:00 and 10:00 .

    The maximum level of noise is (Leq = 82.97 dB) at 08:00. The Leq = 82.97

    dB is less than Leq = 85 dB , so that, this area is suitable for human hearing.

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