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    EXPOSURE TO VEHICULAR

    POLLUTION AND RESPIRATORY

    HEALTH STATUS OF

    THE URBAN INHABITANTS OF

    KOLKATA: A CROSS SECTIONAL

    DISTRIBUTION

    A THESIS SUBMITTED AS A PARTIAL FULFILLMENT OF

    THE REQUIREMENTS FOR THE DEGREE OF

    MASTER OF SCIENCE

    IN

    ENVIRONMENTAL SYSTEM MANAGEMENT

    OF PRESIDENCY COLLEGE, KOLKATA

    (AUTONOMOUS)

    UNDER THE UNIVERSITY OF CALCUTTA

    2009

    Submitted By

    MURARI MOHAN MANNA

    Registration No. 063730 of 2004-05

    DEPARTMENT OF APPLIED GEOLOGY &

    ENVIRONMENTAL SYSTEM MANAGEMENT

    PRESIDENCY COLLEGE, KOLKATA

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    ACKNOWLEDGEMENT

    I feel immense pleasure in expressing my sense of gratitude and gratefulness to

    Dr.H.N.Bhattacharya, Professor and Departmental Head, Department of Applied

    Geology and Environmental System Management, Presidency College, Kolkata, for kind

    permission to allow me to perform this project work in the department and giving

    valuable suggestions to complete the entire study.

    I convey my regards, sincere gratitude and gratefulness to Dr. Saradindra

    Chakraborty, Departmental coordinator and Reader, Department of Environmental

    System Management, Presidency College, Kolkata for his overall guidance and

    constructive criticism to perform this project work and giving the valuable suggestions inentire study.

    I am thankful to the Director, National Institute of occupational health, (NIOH),

    Ahmedabad and officer in charge, Regional Occupational Health Centre (Eastern),

    Kolkata for providing infrastructural facility and according permission for carrying out

    the study in the esteemed institute.

    I convey my great regards, sincere gratitude and gratefulness to Dr. B.P.

    Chattopadhyay, Scientist Emeritus of Respiratory Physiology Division Regional

    Occupational Health Centre (E), Indian Council of Medical Research (ICMR), Block-DP

    Sec-V, Salt Lake, and Kolkata-700091 for his guidance, supervision, realistic criticism

    and valuable suggestion of this project. I am really indebted to you Sir.

    I also convey my regards, sincere gratitude and gratefulness to Dr. Subrata Ghosh,

    Reader, Department of physiology & Environmental System Management, Presidency

    College, Kolkata for his guidance to perform this project work and giving the valuable

    suggestion in the entire study.

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    I express my deepest gratitude to Mubaraq Hossain (Research Scholar), Sk. Jane

    Alam (Technician) and Tilak Kanti Dasgupta (Lab Assisstant) Respiratory physiology

    division of R.O.H.C (E) for their co-operation and encouragement throughout the entire

    project work.

    I am truly grateful to the inhabitants of Kolkata whom I have studied for their

    voluntary cordial cooperation and successful completion of the work. Their kind

    cooperation is thankfully acknowledged.

    Lastly I convey my thanks to all of my friends and batch mates for their heartily co-

    operation and continuous encouragement through out the study.

    Date: 01.06.2009 MURARI MOHAN MANNA

    Department of Applied Geology

    and Environmental System

    Management

    Presidency College

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    Introduction:-

    Since the onset of the industrial revolution, there has been a steady change in the

    composition of the atmosphere mainly due to the combustion of fossil fuels used for the

    generation of energy and transportation. Air pollution is a major environmental health

    problem affecting the developing and the developed countries alike. The effects of air

    pollution on health are very complex as there are many different sources and their

    individual effects vary from one to the other.

    Air pollution has been aggravated by developments that typically occur as

    countries become industrialized: growing cities, increasing traffic, rapid economic

    development and industrialization, and higher levels of energy consumption. The high

    influx of population to urban areas, increase in consumption patterns and unplannedurban and industrial development has led to the problem of air pollution. Currently, in

    India, air pollution is widespread in urban areas where vehicles are the major contributors

    and in a few other areas with a high concentration of industries and thermal power plants.

    Vehicular emissions are of particular concern since these are ground level sources and

    thus have the maximum impact on the general population. Also, vehicles contribute

    significantly to the total air pollution load in many urban areas.

    The behaviour of the particles and gases in the respiratory system is greatly

    influenced by the region of the lung in which they are located. After the air is channelized

    through the trachea to the first bronchi the air is divided at each subsequent bronchial

    bifurcation until very little apparent flow is occurring within the alveolar sacs. Because of

    the very different flows in the various sections of the respiratory region, particles

    suspended in air and gaseous air pollutants are treated differently in the lungs. For

    gaseous pollutants released from automobiles, solubility controls removal from the air

    stream. Highly soluble gases like SO2 are absorbed in the upper airways , whereas less

    soluble gases like NO2, O3 may penetrate to the pulmonary region .Irritant gases are

    thought to stimulate neuroreceptors in the respiratory walls and cause a variety of

    responses including sneezing, coughing, broncho-constriction and rapid shallow

    breathing.(1)

    Many studies have shown links between pollution and health effects. Increases in

    air pollution have been linked to decreases in lung function, neurological impairments

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    and increases in heart attacks. High levels of air pollution directly affect people with

    asthma and other types of lung or heart disease (according to the EPA Air Quality Index).

    The elderly and children are especially vulnerable to the effects of air pollution in

    large metropolitan cities like Kolkata.

    The level of risk depends on several factors:

    The amount of pollution in the air,

    The amount of air we breathe in a given time

    Our overall health.

    Other, less direct ways people are exposed to air pollutants are:

    eating food products contaminated by air toxins that have been deposited where

    they grow,

    drinking water contaminated by air pollutants,

    Ingesting contaminated soil, and touching contaminated soil, dust or water.

    The pollution in Kolkata is further aggravated by usage of adultered fuel by the

    two-stroke auto-rickshaws. Thousands of these auto-rickshaws fleet plies crisscrossing

    the city caring a fig to the Pollution guidelines and health safety of the inhabitants of the

    city. Considering the environmental pollution of the city the respiratory health status of

    the population is very much essential to be evaluated. Considering the above facts the

    present study was undertaken to evaluate the respiratory function status of the inhabitants

    of Kolkata. The respiratory function status of the inhabitants is also to be assessed among

    according to their age, duration of stay on that area and smoking habit.

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    Review of Literature:-

    The combustion in the diesel engine produces soot along with smoke. Soot

    consists of aggregates of spherical primary particles that form in the combustion

    chamber, grow by agglomeration and are emitted as clusters having average particle

    diameter ranging from 0.1-0.5 micrometer (2).As released to the environment, the

    portions of the mass of the diesel soot consisting of adsorbed organic matter can range

    from 5-90 percent (3). Values of 10-15% are representative of modern engines under

    most operating conditions. The size of the diesel soot particles makes it easily respirable

    .Approximately 20-30 % of the inhaled particles in diluted exhaust can be expected to

    deposit in the lungs and airways of humans (4).Regarding the carcinogenicity of diesel

    exhaust, however results from animals have not proved to be very helpful becauseessentially the same lung tumor response is obtained with pure carbon soot and other

    inert particles as with diesel exhaust at comparable mass concentration (5).When bound

    to soot or to haematite, pure chemical carcinogens such as benzo-alpha-pyrene known to

    be present in polluted air have been shown to be carcinogenic for lungs of rodents by

    intertracheal instillations.(6).In US , the EPA has concluded that diesel particulate is a

    probable human carcinogen. The International Agency for Research on Cancer (IARC)

    concluded that diesel exhaust is a probable human carcinogen (7). California in 1998

    listed diesel exhaust as a toxic air contaminant (California, EPA, 1998)

    The important contaminants of the automobile exhausts are oxides of nitrogen

    (NOx), CO, hydrocarbons, respirable particles, sulphur dioxide and volatile organic

    compounds. Increased Volatile Organic Compounds (VOCs) in ambient air of urban

    areas observed because of vehicular exhausts, petrol bunk emissions and industrial

    activities prevailing within the areas (8). Ulvarson et al (9) established the reduction of

    FVC, FEV1 in vehicular exhaust exposed persons and causing obstructive type of PFT

    changes. Nakai et al (10) stated the personal exposure of NO2 concentrations decreased as

    distance from the roadside is increased. Laxen and Noordally (11) assessed the major

    pollutant NO2 arising from automobile exhausts at a street in London and the

    concentration declined as the distance from the road increased. Chattopadhyay et al. (12)

    stated the decrement of PFT values with the synergistic effect of age and automobile

    exposures. The gaseous pollutants and VOCs are mainly formed due to fuel adulteration,

    keeping the vehicles in running condition and traffic density (8). Rao et al (13) revealed

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    that exposure to auto exhaust pollutants caused both restrictive and obstructive type of

    respiratory impairments. Some studies have already reported the health risks like

    increased mortality, morbidity rates and hospital admission due to cardio respiratory

    disease, oxidative stress and increase the incidence of cancer among urban population

    (14, 15, 16, 9).

    Rao et.al (17) reported various volatile hydrocarbons including benzene in ambient air of

    industrial areas in New Mumbai. Srivastava et.al (18) identified more than sixty VOC

    species in Delhi air at residential, commercial and industrial areas. Pandit et.al (19)

    showed that about 10 % of the C2-C5 hydrocarbons are emitted from auto-exhaust in

    Mumbai. Ingle et.al (20) reported ambient air levels of pollutants like SO2, NOx and

    PM10 in traffic areas of Jalgaon and significant reduction in pulmonary function test

    values, particularly the FEV1 and PEFR among traffic police.

    One study demonstrated that children inhaling grossly polluted air of Calcutta

    suffer from adverse lung reactions and genetic abnormality in the exposed tissues. The

    potential health hazards associated with inhalation of airborne pollutants are now well

    recognized. In this context, children are reported to be more susceptible to environmental

    exposures than adults An estimated 4 million children in developing countries die each

    year from respiratory diseases which are potentially preventable and/or treatable. In

    addition, some of the adverse effects of air pollution may be obvious in the adult owing

    to the prolonged latent period (21). Some 70% of people in the city of Calcutta suffer

    from respiratory disorders caused by air pollution, a recent study by a prominent cancer

    institute in India has concluded. The city of Kolkata ranks highest in the country in terms

    of pollution. Ailments include lung cancer, breathing difficulties and asthma, the

    Chittaranjan National Cancer Institute (CNCI) study says. (22) .Diesel soot emitted from

    automobiles is carbon compound coated with organic matter are generally less than 1

    micron in diameter and can penetrate in the lower portions of the lungs. (23).Suspended

    particulate matter is one of the most critical air pollutants in most of the urban areas of

    India and permissible standards are grossly violated frequently (24)

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    Aims and objectives:

    The Study was conducted with the following aims and objectives.

    To evaluate pulmonary function status of the inhabitants of Kolkata.

    To assess the PFT according to their age, duration of stay and smoking habit.

    To evaluate the respiratory function impairments amongst the inhabitants as a whole.

    To evaluate the respiratory function impairment amongst the inhabitants according totheir duration of stay in their area.

    Comparative analyses of the lung function of North, Central and South Kolkatainhabitants.

    Pic: 5- Two-stroke auto rickshaws are a Pic: 6-City pedestrian, porters, hawkers,major source to the city air pollution. rickshaw pullers are vulnerable groups to

    citys environmental pollution.

    Pic: 7- People working in the open air like food sellersand traffic policemen are at risk of Citys environmental pollution.

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    Materials & Methods:

    Selection of subjects:

    The present study was carried out North, Central and Southern pockets of

    Kolkata. The pulmonary function study was carried out on total 113 inhabitants from the

    three areas. The subjects were classified into broadly three groups North (37), Central

    (35) and South (41).The subjects were selected from 21-50age range from varied

    economic class people.

    Questionnaire method :

    Detailed present and past personal and occupational history was taken.

    Due stress was given to note the smoking history and the frequency of smoking per day.

    Among the inhabitants who smoked at least 5-6 beedi and/or cigarette per day are

    included in the smoking category and those who have not smoked through out their life

    time was considered as non-smoker and those who left smoking are considered as ex-

    smokers. The time of taking personal history of the individuals special attention was

    given to make the respiratory impairments if any.

    Pulmonary Function Test:

    Vital capacity (VC) and Forced Vital Capacity (FVC) was recorded by

    Spirovit SP-10(Pic-15) (Schiller Health Care Pvt Ltd., Switzerland) and Peak Expiratory

    Flow Rate by Wrights Peak Flow meter (Clement and Clarke, UK). Forced expiratory

    volume in one second (FEV1) Forced expiratory volume in 1st

    sec. as the percentage of

    FVC (FEV1%), forced expiratory flow at 200 ml 1200 ml, 25 75% and 75 85% was

    calculated from the tracings. Before the recordings were taken all subjects were made

    well motivated thus ensuring recording at optimum levels. The PFT measurements were

    made in a comfortable standing position. The body height and body weight were

    measured with a standard scale without footwear. All measured lung volumes obtained

    was expressed in body temperature pressure saturated with water vapour (BTPS). Body

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    surface area (BSA) was calculated from the Du-Bois and Du-Bois formula. Pulmonary

    function test values were predicted from the standard prediction equation of the Kolkata

    normal subjects. The criteria followed for categorization of the severity of restrictive

    impairment are based upon the ratios between predicted and observed values of VC and

    obstructive impairment based of FEV1%.

    Statistical Analysis:

    Student two tailt tests are being performed by the inhabitants to find

    whether there are any significant changes due to duration of staying at that area.

    Formulae Used:

    BMI = Weight in Kg / (Height in Metre)2

    BSA = (Height in cm) * 0.725*(Weight in Kg) * 0.425 * 71.84 / 10000

    Criteria for Determination of Obstructive Type Impairment:

    Obstructive Type Impairment is determined with respect to the FEV1% value.

    Normal 70%

    Mild Obstructive 65-69.99%

    Moderate Obstructive 50-64.99%

    Severe Obstructive 49.99%

    Criteria for Determination of Restrictive Type Impairment:

    Restrictive Type Impairment is determined with respect to the SVC

    For male (Predicted SVC value) -0.024 * age + 0.044 * height in cm - 2.704

    For female (Predicted SVC Value) -0.025 * age + 0.021 * height in cm 0.003

    (Predicted SVC Value Observed SVC Value)*100/Predicted SVC Value

    Up to 20 Normal

    20.01-30 Mild Restrictive Type

    30.01-40 Moderate Restrictive Type

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    40.01 Severe Restrictive Type

    Terminology and Definitions of Static and Dynamic PFT

    parameters:-

    Static PFT parameters:-

    TV Tidal Volume The respiratory excursion for each breadth.

    SVC - Slow vital capacity - This test is performed by having the patient slowly and

    completely blows out all the air from the lungs.

    IC Inspiratory Capacity - The volume of gas that can be taken into the lungs in a full

    inhalation, starting from the resting inspiratory position; equal to the tidal volume plus

    the inspiratory reserve volume.

    IRV - Inspiratory Reserve Volume Maximum Volume that can be inspired is beginning

    from the position of resting inspiration.

    ERV - Expiratory Reserve volume Volume which can be expired by a maximum effort

    beginning at the position of resting expiration.

    Dynamic PFT parameters:-

    FVC - Forced Vital Capacity - after the subject has taken in the deepest possible

    inspiration, this is the volume of air which can be forcibly and maximally exhaled out of

    the lungs until no more can be expired. FVC is usually expressed in units called liters.

    This PFT value is critically important in the diagnosis of obstructive and restrictive

    diseases.

    FEV1 - Forced Expiratory Volume in One Second - this is the volume of air which can be

    forcibly exhaled from the lungs in the first second of a forced expiratory maneuver. It is

    expressed as liters. This PFT value is critically important in the diagnosis of obstructive

    and restrictive diseases.

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    FEV1/FVC - (FEV1%) - This number is the ratio of FEV1 to FVC - it indicates what

    percentage of the total FVC was expelled from the lungs during the first second of forced

    exhalation - this number is called FEV1%, %FEV1 or FEV1/FVC ratio. This PFT value is

    critically important in the diagnosis of obstructive and restrictive diseases.

    FEV3- Forced Expiratory Volume in Three Seconds - this is the volume of air which can

    be forcibly exhaled in three seconds - measured in Liters - this volume usually is fairly

    close to the FVC since, in the normal individual, most of the air in the lungs can be

    forcibly exhaled in three seconds.

    FEV3/FVC FEV3%- This number is the ratio of FEV3 to the FVC - it indicates what

    percentage of the total FVC was expelled during the first three seconds of forced

    exhalation. This is called %FEV3 or FEV3%.

    PEFR - Peak Expiratory Flow Rate - this is maximum flow rate achieved by the patient

    during the forced vital capacity maneuver beginning after full inspiration and starting and

    ending with maximal expiration - it can either be measured in L/sec or L/min - this is a

    useful measure to see if the treatment is improving obstructive diseases like broncho

    constriction. This parameter can be studied by Wrights Peak Flow Meter and expressed

    in l/min.

    FEF - Forced Expiratory Flow - Forced expiratory Flow is a measure of how much air

    can be expired from the lungs. It is a flow rate measurement. It is measured as

    liters/second or liters/minute. The FVC expiratory curve is divided into quartiles and

    therefore there is a FEF that exists for each quartile. The quartiles are expressed as

    FEF25%, FEF50%, and FEF75% of FVC.

    FEF 25% - This measurement describes the amount of air that was forcibly expelled in the

    first 25% of the total forced vital capacity test.

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    FEF 50% - This measurement describes the amount of air expelled from the lungs during

    the first half (50%) of the forced vital capacity test. This test is useful when looking for

    obstructive disease. The amount of air that will have been expired in an obstructed patient

    is smaller than that measured in a normal patient.

    FEF.2-1.21- Forcefully expiratory flow rate during expired air 200ml to 1200ml of the

    forced vital capacity test.

    FEF25%-75% - This measurement describes the amount of air expelled from the lungs

    during the middle half of the forced vital capacity test. Many physicians like to look at

    this value because it is an indicator of obstructive disease.

    FEF75-85% - Lung flow rate during expiration of 75% to 85% of the forced vital capacity

    test.

    MVV - Maximal Voluntary Ventilation - this value is determined by having the patient

    breathe in and out as rapidly and fully as possible for 12 -15 seconds - the total volume of

    air moved during the test can be expressed as L/sec or L/min - this test parameter reflects

    the status of the respiratory muscles, compliance of the thorax-lung complex, and airway

    resistance

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    Pic: 11- Taking personal history of the subjects using Pic: 12 Stadiometer (height

    standard proforma by questionnaire method. and weight measurement).

    Pic: 13- Measurement of weight and height of subjects using Stadiometer.

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    values in height (male-159.72cm, female-149.94cm), weight(male-54.94Kg, female-

    46.59 Kg), body surface area(male-1.56 m2 , female-1.39 m2 ), body mass index (male

    21.42, female 20.59)

    In South Kolkata, the mean age of male and female individuals are 34.52(8.53)

    and 34.95(7.34) respectively. Because of the sex difference males have higher mean

    values in height (male-166.33cm, female-148.45cm), weight(male-62.76Kg, female -

    53.50 Kg),body surface area(male-1.69 m2

    , female-1.46 m2

    ).The body mass index

    showed higher values in females (male 22.74, female 24.3)

    Significant changes have been observed in the height and body surface area

    between the inhabitants of Central Kolkata male and South Kolkata male and in body

    mass index when compared Central Kolkata female with South Kolkata females. The

    statistical analyses were carried out separately in the two sexes.

    Pulmonary function Tests (PFT) of the study population are presented in Table-3

    and Fig:2, 3 and 4. The male subjects are having higher mean values in lung volumes and

    flow rates compared to the female inhabitants.

    Table:-3: Lung volume and flow rates of male and female inhabitants of north,

    central and south Kolkata (Mean SD)

    [* p

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    The SVC, FEF25-75% and FEF75-85 % values of Central Kolkata male population

    has been found to be statistically lower than South Kolkata males. The SVC, FVC and

    FEV1 values of Central Kolkata female inhabitants have been found to be statistically

    lower as compared to North Kolkata females. The PEFR value of North Kolkata female

    population has also been statistically found to be higher than South Kolkata females. In

    general the lung volume and flow rates of South Kolkata population have been observed

    to be better than North Kolkata and the values of Central Kolkata population have been

    found to be the least.

    .

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    The PFT values of male inhabitants according to their duration of stay in theregion have been given in Table-4 and fig 5-11.All the subjects were classifiedaccording to their duration of stay in the area into four groups as: up to 20, 21-30, 31-40,41-50.

    Table:-4: Lung volumes and flow rates of male individual according to duration of

    stay in north, central and south Kolkata (Mean SD)

    Category Duration

    of stay

    (Yrs)

    SVC

    (l)

    FVC

    (l)

    FEV1(l)

    FEV1% FEF.2-

    1.21ml

    (l/s)

    FEF25-

    75%

    (l/s)

    FEF75-

    85% (l/s)

    PEFR

    (l/min)

    Up to 20(n=0)

    - - - - - - - -

    21-30(n=8)

    3.920.35

    4.170.56

    3.650.43

    87.672.97

    6.601.73

    4.581.06

    1.970.79

    462.50117.81

    31-40

    (n=8)

    3.51

    0.56

    3.72

    0.79

    3.04

    0.81

    81.26

    8.24

    6.20

    1.95

    3.22

    1.49

    1.06

    0.64

    453.75

    130.81

    North

    Kolkata

    Male

    (n=21)

    41-50(n=5)

    2.55**0.89

    2.64*1.19

    2.02**0.98

    74.95*12.33

    3.782.56

    1.97***0.61

    0.59***0.26

    344.00154.37

    Up to 20(n=5)

    3.620.52

    3.740.49

    3.180.69

    84.409.96

    6.562.36

    3.601.42

    1.320.49

    472.0081.98

    21-30(n=5)

    3.200.09

    3.240.12

    2.740.26

    84.405.18

    5.390.76

    3.011.01

    1.100.38

    406.0053.20

    31-40(n=6)

    3.290.50

    3.240.46

    2.850.33

    88.172.64

    5.921.69

    3.390.61

    1.230.17

    430.0064.50

    Central

    Kolkata

    Male

    (n=18)

    41-50(n=2)

    3.320.92

    3.261.00

    2.780.74

    86.004.24

    6.720.59

    3.390.23

    0.900.08

    480.000

    Up to 20(n=1)

    4.53 4.60 3.75 82.00 6.25 3.47 1.68 400.00

    21-30(n=7)

    4.280.96

    4.230.99

    3.820.86

    90.626.91

    7.811.37

    4.911.35

    2.010.86

    532.8670.17

    31-40(n=6)

    3.741.04

    3.581.48

    3.241.41

    86.8711.18

    6.623.23

    4.582.11

    1.860.95

    478.33187.87

    SouthKolkata

    Male

    (n=21)

    41-50(n=7)

    3.390.66

    3.610.54

    3.000.54

    82.886.40

    6.692.22

    3.110.87

    1.160.54

    437.14126.06

    [* p

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    Fig-8: Different flow rates of north Kolkata male

    inhabitants according to duration of stay

    0

    1

    2

    3

    4

    56

    7

    up to 20 21-30 31-40 41-50

    Stay range distribution

    Flow

    rates(l/sec

    )

    FEF.2-1.21ml (l/s)

    FEF25-75%(l/s)

    FEF75-85% (l/s)

    Fig-9: Different flow rates of central Kolkata maleinhabitants according to duration of stay

    0

    2

    4

    6

    8

    up to 20 21-30 31-40 41-50

    Stay range distribution

    Flow

    rates(l/sec)

    FEF.2-1.21ml (l/s)

    FEF25-75%(l/s)

    FEF75-85% (l/s)

    Fig-10: Different flow rates of south Kolkata male

    inhabitants according to duration of stay

    0

    2

    4

    6

    8

    10

    Up to 20 21-30 31-40 41-50

    Stay range distribution

    Flow

    rates

    (l/sec)

    FEF.2-1.21ml (l/s)

    FEF25-75%(l/s)

    FEF75-85% (l/s)

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    Fig-11: PEFR of Kolkata male inhabitants

    according to duration of stay

    0

    100

    200

    300

    400500

    600

    up to 20 21-30 31-40 41-50

    Stay range distribution

    PEFR(l/min)

    North Kolkata male

    Central Kolkata male

    South Kolkata male

    It has been observed that there is a gradual trend of decrement of lung volume and

    flow rates with the increase of duration of stay in the respective areas.

    Among the North Kolkata males there is a significant decrement of the SVC,

    FVC, FEV1, FEV1%, FEF25-75%, FEF 75-85% values of the individuals residing in the area

    residing for 41-50 years as compared to residents residing in the area for 21-30 years.

    There is also a significant decrement of the FEF75-85 % value of the subjects residing for

    41-50 years as compared to subjects residing for 31-40 years. Among the Central Kolkata

    males there is a significant decrement of the FEF75-85% value of the subjects residing for

    41-50 years as compared to subjects residing for 31-40 years. Among the South Kolkata

    males there is a significant decrement of the FEF 25-75% value of the subjects residing for

    41-50 years as compared to subjects residing for 31-40 years.

    The SVC, FVC and FEV1 values of Central Kolkata in the age group of 21-30 has

    been found to be significantly lower than their North Kolkata and South Kolkata

    counterparts. In the 31-40 age group the FEV1% mean value of North Kolkata inhabitants

    has been found to be significantly lower than the Central Kolkata inhabitants of the same

    age group. In the age group of 41-50 the FEF25-75% and FEF75-85% of North Kolkata maleinhabitants have been found to be significantly lower than the South Kolkata inhabitants.

    The FEF25-75% value of North Kolkata inhabitants of the same age group has also been

    found to be significantly lower than the Central Kolkata male population of the same age

    group.

    The PFT values offemale inhabitants according to their duration of stay in the

    area have been given in Table-5 and fig: 12-18. All the subjects were classified

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    Fig-12: Lung volume of north Kolkata female

    inhabitants according to duration of stay

    0

    0.5

    1

    1.5

    2

    2.53

    3.5

    Up to 20 21-30 31-40 41-50

    Stay range distribution

    litres

    SVC (l)

    FVC (l)

    FEV1 (l)

    Fig-13: Lung volume of central Kolkata femaleinhabitants according to duration of stay

    0

    0.5

    1

    1.5

    2

    2.5

    3

    Up to 20 21-30 31-40 41-50

    Stay range distribution

    litres

    SVC (l)

    FVC (l)

    FEV1 (l)

    Fig-14: Lung volume of south Kolkata female

    inhabitants according to duration of stay

    0

    0.5

    1

    1.52

    2.5

    3

    3.5

    Up to 20 21-30 31-40 41-50

    Stay range distribution

    litres

    SVC (l)

    FVC (l)

    FEV1 (l)

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    Fig-15: Different flow rates of north kolakta female

    inhabitants according to duration of stay

    0

    1

    2

    3

    45

    6

    up to 20 21-30 31-40 41-50

    Stay range distribution

    Flow

    rates(l/sec

    )

    FEF.2-1.21ml (l/s)

    FEF25-75% (l/s)

    FEF75-85% (l/s)

    Fig-16: Different flow rates of central Kolkata

    female inhabitants according to duration of stay

    0

    1

    2

    3

    4

    5

    up to 20 21-30 31-40 41-50

    Stay range distribution

    Flow

    rates(l/sec)

    FEF.2-1.21ml (l/s)

    FEF25-75% (l/s)

    FEF75-85% (l/s)

    Fig-17: Different flow rates of south Kolkata

    female inhabitants according to duration of stay

    0

    1

    2

    3

    4

    5

    up to 20 21-30 31-40 41-50

    Stay range distribution

    Flow

    rates(l/sec)

    FEF.2-1.21ml (l/s)FEF25-75% (l/s)

    FEF75-85% (l/s)

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    Fig-18: PEFR of Kolkata female inhabitants

    according to duration of stay

    0

    100

    200

    300

    400

    up to 20 21-30 31-40 41-50

    Stay range distribution

    PEFR(l/min)

    North Kolkata female

    Central Kolkata female

    South Kolkata female

    It has been observed that there is a gradual trend of decrement of lung volume and

    flow rates with the increase of duration of stay in the respective areas.

    Among the Central Kolkata females there is a significant decrement in the SVC,

    FVC and PEFR values of the resident duration range of 21-30 years as compared to the

    group staying up to 20 years. Among the South Kolkata females there is a significant

    decrement in the SVC value of the resident duration range of 41-50 years as compared to

    the group staying up to 21-30 years.

    In the age group of 21-30 the SVC, FVC, FEV1, FEF.2-1.21ml and PEFR of North

    Kolkata and SVC, FVC, FEV1 of South Kolkata have been found to be significantly

    higher than the population of Central Kolkata .

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    The PFT values of male inhabitants according to their age distribution in the

    region have been given in Table-6 and fig: 19-25.All the subjects were classified

    according to their age into three groups: 21-30, 31-40, 41-50.It has been observed that

    there is a gradual trend in the decrement of the lung volume and flow rates of the subjects

    with age.

    Table:-6: Lung volumes and flow rates of male individual according to age range

    (Mean SD)

    [* p

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    Fig-27: Lung volume of north Kolkata female

    inhabitants according to age distribution

    0

    0.5

    1

    1.5

    2

    2.5

    3

    3.5

    21-30 31-40 41-50

    Age range distribution

    litres

    SVC

    FVC

    FEV1

    Fig-28: Lung volume of central Kolkata femaleinhabitants according to age distribution

    0

    0.5

    1

    1.5

    2

    2.5

    3

    21-30 31-40 41-50

    Age range distribution

    litres

    SVC

    FVC

    FEV1

    Fig-29: Lung volume of south Kolkata female

    inhabitants according to age distribution

    0

    0.5

    1

    1.52

    2.5

    3

    3.5

    21-30 31-40 41-50

    Age range distribution

    litres

    SVC

    FVC

    FEV1

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    Fig-30: Different flow rates of north Kolkata female

    inhabitants according to age distribution

    0

    1

    2

    3

    4

    5

    21-30 31-40 41-50

    Age range distribution

    Flowr

    ate(l/sec)

    FEF.2-1.21ml (l/s)

    FEF25-75% (l/s)

    FEF75-85% (l/s)

    Fig-31: Different flow rates of central Kolkata femaleinhabitants according to age distribution

    0

    1

    2

    3

    4

    5

    21-30 31-40 41-50

    Age range distribution

    Flowr

    ate(l/sec)

    FEF.2-1.21ml (l/s)

    FEF25-75% (l/s)

    FEF75-85% (l/s)

    Fig-32: Different flow rates of south Kolkata female

    inhabitants according to age distribution

    0

    1

    23

    4

    5

    21-30 31-40 41-50

    Age range distribution

    Flow

    rate(l/sec)

    FEF.2-1.21ml (l/s)

    FEF25-75% (l/s)

    FEF75-85% (l/s)

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    The PFT values according smoking habit are represented in Table-8 and Fig-33-

    36. The PFT values of the smokers are slightly higher compared to the non-smoker in

    several parameters.

    Table: - 8:-Lung volume and flow rates of male subjects according to their smokinghabits (Mean SD)

    [No statistically significant difference in the values has been observed]

    No statistical significant variation has been observed in the

    pulmonary function tests of various parameters between the smokers and the non-

    smokers of the different areas but variations in the mean values have been observed.

    Among the North Kolkata males the mean values of SVC, FVC,

    FEF.2-1.21 and PEFR have been found to be higher in the smokers in comparison to that of

    the non-smokers. Similarly among the Central Kolkata subjects the mean values of SVC

    and FVC have been found to be higher in the smokers than in the non-smokers. Likewise

    in South Kolkata all the PFT parameters have been found to be higher in the smokers as

    compared to the non-smokers.

    A number of reasons may be cited to explain this anomalous variation by the fact

    that only small number of individuals (n) have been studied i.e the numbers of smokers

    CategoryDuration

    of stay

    (Yrs)

    BSA BMI SVC

    (l)

    FVC

    (l)

    FEV1(l)

    FEV1% FEF.2-

    1.21ml

    (l/s)

    FEF25-

    75%

    (l/s)

    FEF75-

    85%

    (l/s)

    PEFR

    (l/min)

    Non-Smoker(n=13)

    1.660.19

    24.073.38

    3.420.85

    3.631.04

    3.100.98

    83.999.46

    5.712.40

    3.821.45

    1.470.89

    430.00143.99

    North

    Kolkata

    (n=21)Smoker(n=8)

    1.60.19

    20.95.06

    3.470.70

    3.640.96

    2.410.93

    79.28.2

    5.892.11

    2.831.53

    1.010.71

    432.50127.25

    Non-Smoker(n=14)

    1.550.16

    21.262.63

    3.340.48

    3.380.51

    2.930.47

    86.794.04

    6.171.24

    3.460.89

    1.220.35

    452.1462.04Central

    Kolkata

    (n=18) Smoker(n=4)

    1.580.20

    21.994.37

    3.440.47

    3.390.45

    2.800.52

    82.5010.66

    5.592.75

    3.031.19

    1.040.33

    400.0071.18

    Non-Smoker(n=14)

    1.660.17

    21.674.41

    3.720.98

    3.731.09

    3.291.07

    86.378.94

    6.772.37

    4.041.69

    1.660.91

    476.43142.70

    South

    Kolkata

    (n=21) Smoker

    (n=7)

    1.76

    0.15

    24.86

    5.35

    4.07

    0.80

    4.11

    0.89

    3.56

    0.78

    86.86

    7.66

    7.52

    2.01

    4.36

    1.48

    1.69

    0.69

    484.29

    111.93

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    are very low in comparison to the non-smokers and they had better lung function values

    than the non-smokers. From the given table it is observed that the mean values of BSA

    and BMI of the smokers are higher than the non-smokers, as the thoracic cavity and the

    body surface area of their body are higher they have a greater possibility to have more

    lung volume and hence better flow rates. The smoking factor also depends on the number

    of beedi/cigarettes smoked per day, duration of smoking and the number of puffs taken

    each time.

    Fig-33: Distribution of male Kolkata inhabitants

    according to their smoking habit

    0

    2

    4

    6

    8

    10

    12

    14

    16

    North Kolkata Central Kolkata South Kolkata

    Numbers

    NON-SMOKER

    SMOKER

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    Conclusion:-

    The health effect of environmental pollution has been a great concern for mankindsince several decades. In the developing countries industrial emission continues to be the

    major source of air pollution but with the increasing number of vehicles, vehicular air

    pollution is becoming increasingly important especially in the metropolitan city, Kolkata

    is one of the polluted cities in India as per the CPCB. The pollution level showed a rising

    trends from day to day. This is confirmed by the Lung function impairment data of the

    inhabitants only due to the exponential vehicular pollution rise. This produces rise in

    SPM and other pollutant levels in residential, commercial area. Urbanization creates

    pollution. The 3 Ps- Population, Poverty and pollution are quite interlinked with one

    another. Population explosion at Kolkata because of new births and migration is the most

    vital reason for deterioration of the environment.

    Vehicles pollution occurs due to:-

    Unscrupulous use of Adultered Fuel.

    Poor maintenance of the vehicles.

    Faulty Driving techniques.

    Road borne dust.

    Age of the vehicle and its present roadworthiness.

    Miscellaneous-

    Open burning of garbage, running of generator sets, burning of

    tyres etc.

    Road side dust.

    Construction activities.

    Effect of deplantation.

    Meteorological conditions.

    The people residing in the city are exposed to that environment. The

    particular populations residing nearer to the main traffic junction or by the side of the

    main roads of the city are very much exposed to the automobile exhausts. Rapid increase

    of number of vehicles, vehicular air pollution is becoming increasingly important

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    Recommendation:-

    In the context to the present study some ideas and suggestions for possible

    management of environmental pollution of Kolkata air can be forwarded- .

    The burning of fuel is major source of pollution so the possible measure should be

    the replacement of burning fossil fuel by electricity or solar energy or by improvement of

    the fuel quality and fuel burning process. There are number of mechanical devices that

    might be helpful for reduction of pollutant emission level from different industries and

    other sources.

    Since vehicles contribute significantly to the total air pollution load in most urban

    areas, vehicular pollution control deserves top priority. A practical strategy should be

    devised that reduces both emissions and congestion. Some of these strategies may be Phase out the all vehicles older than ten to fifteen years, two and three wheelers

    should have four stroke engines with catalytic converter and fuelled by Biodiesel, LPG or

    CNG. Catalytic Converters convert comparatively more toxic CO and Hydrocarbons to

    less toxic CO2 and water. In addition to these fuels, use of diesel fuel with lower sulfur

    content can help to reduce emissions. A newer vehicle that meets more stringentemission standards is purchased to replace the scrapped vehicles.

    Bharat Stage IV norms should be enforced on all vehicles and smooth movement

    of vehicles should be facilitated by construction of new flyover, bridges, improvement of

    road condition and width of the roads. Mass Rapid Transport System may be considered

    for the fast expanding and major urban cities like Kolkata. Greater promotion and use of

    alternative fuels such as CNG/LPG/Propane/ battery operated vehicles. Expansion of

    CNG dispensing facilities and increased fiscal incentives for CNG kits should be

    encouraged. Taxes on fuels, vehiclesthe revenue so generated could be used for

    pollution control measures. Strengthening of inspection and maintenance (I&M) system:

    The I&M system, comprising inspection, maintenance, and certification of vehicles, is

    crucial for regulating pollution for the large fleet of in-use vehicles. It should include

    testing of various elements of safety, road worthiness and compliance to pollution norms.

    Diversion of heavy goods traffic in peak hours is very much essential to

    minimize the automobile pollution and the pollution of the city as a whole. Use of Public

    Vehicles should be encouraged as it saves not only fuel but also the load of city ambient

    air pollution. Plantation at the city road side is essential to reduce the suspended

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    (14) Dockery DW, Pope CA IV, Xu X, Spengler JD, Ware JH, Fay ME, Ferris BG,,

    Spiezer FE (1993).An Association between air pollution and mortality in six US

    cities. The New England Journal of Medicine 329: pp1753-1759.

    (15) Padhy PK, Varshney CK (2000) Total non methane volatile organic compounds

    (TNMVOC) in the atmosphere of Delhi. Atmospheric Environment 34: pp577-

    584.

    (16) Samet J, Domonici F, Curriero C, Coursac I, Zeger SL (2000) Fine particulate Air

    Pollution and Mortality in 20 US cities,1987-1994,The New England Journal of

    medicine 343:pp1742-1749.

    (17) Rao MA, Pandit GG, Sain P, Sharma S, Krishnamoorthy TM, Nambi KSV

    (1997). Non methane Hydrocarbon in Industrial location of Bombay atmospheric

    environment 31(7) :pp1077-1085.

    (18) Srivastava A, Joseph AE, Patil S, More A, Dixit RC, Prakash M (2005) Air toxics

    in ambient air of Delhi. Atmospheric Environment 39: pp59-71.

    (19) Pandit GG, Mohon Rao AM (1990) Evaluation of auto exhaust contribution to

    atmospheric C2-C5 hydrocarbonat Deoner, Bombay. Atmospheric Environment

    24A: pp811-813

    (20) Ingle ST, Pachpande BG, Wagh ND, Patel VS, Attarde SB (2005) Exposure to

    vehicular pollution and Respiratory Impairment of Traffic Policemen in Jalgaon

    City, India , Industrial health. 43: pp656-662.

    (21) Lahiri Twisha, Roy Senjuti, Basu Chandreyi, Ganguly Sangeeta, Et al (Jul 2000),

    Indian Journal of Medical Research

    (22) CNCI Report 2007.

    (23) Wei E T, Shu Helen P et.al (September 1983), Nitro aromatic Carcinogens in

    Diesel Soot, Vol. 73, No. 9.

    (24) S. T. Ingle, N. D. Wagh, B. G. Pachpande, V. S. Patel and S. B. Attarde, The

    influence of workplace environment on lung function of shopkeepers working

    near National Highway in Jalgaon: A note. Transporatation Research: Part D,

    2005.

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    Proforma of the project:Proforma of the project:Proforma of the project:Proforma of the project:

    Assessment of the Effects of High Particulate Pollutants on Pulmonary Health

    Status in Selected Mega cities of South Asia

    Area information

    A. Serial no. B. Interviewer:

    C. Air Quality Monitoring Station: D. Distance from the station

    E. Date: F. Room Temperature:

    Part 1. IDENTIFICATION DATA

    01. Identification Number (4 Digits):

    02. Name:

    03. Name of the father/spouse:

    04. Name of the Head of the family

    05. Age:

    06. Sex: (Male - 1, Female - 2)

    07. Address:

    Part 2. GENERAL INFORMATION ON HOUSEHOLD AND FAMILY

    08. Distance from the main road:09. Any local sources of outdoor pollution: (eg. Factory etc):

    10. Floor of residence:

    11. Number of rooms:Kitchen is in the separate room or in the same room-----------------------------------

    Ventilation of the house or room---------Good----------Satisfactory---------------Poor

    Regional Occupational Health Centre

    (Eastern)(Indian Council of Medical Research)

    Block-DP, Sector-V, Salt Lake, Kolkata-700091

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    21. How many bidis/cigarettes etc do you smoke or used to smoke every day?(Maximum no. ever) ------

    22. How many years you smoked-----------------Number of smoker in the family---------------------------

    23. If ex-smoker, reason for stopping: ____________________

    24. PERSONAL HISTORY OF THE SUBJECT.

    Are you suffering from any respiratory or other diseases already diagnose-----------------------------

    If yes specify the name of the disease------------------------------------------------------------------------

    Did you have any periodical illness---------------------------------------------------------------------------?

    Did you have any respiratory problem like cough-------------------------------------------------Yes/ No,

    Specify-------------------------------------------------------------------------------------------------------------

    Did you have any respiratory problem like breathlessness---------------------------------------Yes/ No.

    Specify-------------------------------------------------------------------------------------------------------------

    Did you have any respiratory problem like morning cough--------------------------------------Yes/ No.

    Specify-------------------------------------------------------------------------------------------------------------

    Did you have any respiratory problem like chest tightness--------------------------------------Yes/ No.

    Specify-----------------------------------------------------------------------------------------

    --------------------

    Did you have any respiratory problem like cough through out the day-------------------------Yes/No.?

    Specify-------------------------------------------------------------------------------------------------------------

    Do you have the respiratory problem during seasonal variations?Summer, winter, Rainy etc------------------------------------------------------------------

    -------------------

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    Do you feel any breathlessness: ----------------------------------------------------------------------Yes/No.

    FAMILY HISTORY

    Any of the family members suffer from respiratory disease--------------------------------------Yes/No.

    Relationship with the subject-----------------------------------------------------------------------------------

    If diagnosed name of the disease-------------------------------------------------------------------------------

    A. Physical Characteristics

    Height :______________( cm); Weight :_______________( Kg)

    BSA: _______________ ; BMI: _________________

    B. Static Lung Function Test Values

    (In each parameter selected the best of three simultaneous records)

    a) SVC---------------------- (l) b) ERV------------------------------- (l)

    c) IRV----------------------- (l) d) TV--------------------------------- (ml)

    C. Dynamic Lung Function Test Values:

    (In each parameter selected the best of three simultaneous records)

    (a)FVC------------------------------ (l)

    (b)FEV1----------------------------- (l)

    (c)FEV1/FVC---------------------- (%)

    (d)FEF.2-1.21------------------------- (l/s)

    (e)FEF25-75%-------------------------(l/s)

    (f) FEF75-85%-------------------------(l/s)

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