Aijrfans17 303

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American International Journal of Research in Formal, Applied & Natural Sciences

Available online at http://www.iasir.net

ISSN (Print): 2328-3777, ISSN (Online): 2328-3785, ISSN (CD-ROM): 2328-3793 AIJRFANS is a refereed, indexed, peer-reviewed, multidisciplinary and open access journal published by International Association of Scientific Innovation and Research (IASIR), USA (An Association Unifying the Sciences, Engineering, and Applied Research)

Quantification of increase in Blood pressure due to Urban Air Pollution in terms of AQI with reduction in Forced vital capacity of Lungs. Manish Chawla1, Dr. Vineet Marwaha2, Dr. Suresh Kumar Singh3** 1 Research Scholar J.N.V University, Jodhpur, Rajasthan, INDIA. 2 Dr.Vineet Marwaha, M.D Consultant Radiologist, Max Super Speciality Hospital, IP Extension Delhi, INDIA. 3 Professor, Department of Civil Engineering & Architecture, Faculty of Engineering, J.N.V University, Jodhpur, Rajasthan, INDIA. Abstract: Urban air pollution is a leading problem for environmental health. It is one of the main causes of respiratory problems and selected cardiovascular diseases. Due to damage to respiratory system various pulmonary function values are reduced. Persons with lower pulmonary functions have a higher risk for developing cardiovascular diseases including hypertension. Also air pollution exposure results in significant changes in many cardiovascular indexes like- heart rate, blood pressure etc. As Jodhpur is declared Rajasthan’s most polluted city by W.H.O, we took a study to evaluate association and develop a relationship between increase in blood pressure due to air pollution in terms of Indian AQI as per CPCB and reduction in lung capacity in terms of reduction in forced vital capacity. Five locations at Jodhpur were selected for taking observations of PM10, SO2, NO and CO to evaluate AQI. Study was undertaken on persons with exposure to air pollution for 1-5 years. Persons with the same socio-economic background but not exposed to urban air pollution were selected as control population for comparison. Data related to cardiovascular risk including age, body mass index, weight and height, systolic and diastolic blood pressure was collected. Reduction in forced vital capacity was measured and index was developed to find out the extent of damage in terms of percentage of volume reduction in fraction (IFVC). Blood pressure was measured with the subject seated and percentage increase in systolic blood pressure (ISBP) and percentage increase in diastolic blood pressure (IDBP) was calculated. Regression analysis with the help of SPSS was done to find out the statistical parameters. It is clear from the statistical analysis that independent variable IFVC accounts for the variation in ISBP up to 88.4% and remaining 11.6% is due to other reasons. It also indicates that independent variable account IFVC accounts for the variation in IDBP up to 92.3% and remaining variation is due to other reasons. Estimated equations for showing relationship of ISBP/IDBP with IFVC were developed by multiple regression analysis. Key words: Diastolic blood pressure, systolic blood pressure, Air Quality Index, Forced vital capacity, PM10

I. Introduction Urban air pollution is proving to be a great health hazard for the residents of the cities. Air pollution consists of many gasses pollutants along with varying sizes of particulate matter. These particles are able to penetrate deeply into the respiratory tract and therefore constitute a risk to health by increasing mortality from respiratory infections and diseases like lung cancer and selected cardiovascular diseases2. High respiratory vulnerability has been widely acknowledged as a major component of adverse effects of air pollution3.Several studies have shown an association between lung function decline and long term exposure to air pollution in adults1,5,8. Studies have shown divergent results to explain the effect and the characteristic of the impairment (restrictive or obstructive)10,11.Lately air pollution induced cardiovascular toxicity has become the focus of intensive studies among cardiologists and specialists in environmental medicine2. As the chemical composition of ambient particles varies greatly between different geographical areas, it is difficult to identify specific components that elicit cardiovascular toxicity. Air pollution exposure results in significant changes in many cardiovascular indexes. Some of the effects i.e. changes in heart rate, blood pressure, develop acutely in response to increased level of ambient particles 2. Choi , Xu, Park in their study showed the association between ambient air-pollutant concentrations and blood pressure7. .Engstrom et al. found that the incidence of cardiovascular disease and death associated with hypertension is increased in the presence of reduced lung function4. Studies indicates that blood pressure is also a risk factor for future cardiovascular diseases6,14.Most of the studies have carried out on particular concentration of a specific pollutant and its effect on respiratory system and on blood pressure. All most in all studies either pollutant concentration as variable or exposure duration as a variable was considered and extent of damage were reported as increase of

AIJRFANS 17- 303; Š 2017, AIJRFANS All Rights Reserved

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Suresh Kumar Singh et al., American International Journal of Research in Formal, Applied & Natural Sciences, 19(1), June-August 2017, pp. 07-12

blood pressure or mild/severe damage of respiratory system. Quantification of increase of blood pressure due to urban air pollution is not done in relation to decrease of pulmonary function. In this study efforts have been made to quantify increase in blood pressure in relation with decrease of force vital capacity (FVC), due to urban air pollution in terms of Indian AQI as per Central Pollution Control Board (CPCB) of India. Keeping all this in view, the present cross sectional study is designed to monitor the ambient air quality and correlate it with the respiratory and cardiovascular health status of the general population in Jodhpur. It represents hot and arid climate. It has high amount of dust load and sand in the ambient atmosphere. Due to arid condition in Jodhpur there are frequent dust storm events in pre monsoon season. This leads to long range transport and spread of airborne suspended particulate matter. The aerosols originating naturally (mineral dust) is also one of the important parameter. Jodhpur is the second largest city of Rajasthan and is situated in the western part of Rajasthan (India). According to report by W.H.O in 2014 Jodhpur has the highest concentration of PM 10 in Rajasthan11. Jodhpur is Rajasthan’s most polluted city as per May 2016 report of World Health Organisation13. II.

Methodology & Observations

Various observations for PM10, SO2, NO2 & CO were taken at five locations of Jodhpur. From these concentrations of the pollutants, value of sub indices of respective pollutants were calculated to predict AQI as per CPCB guidelines13. The highest value of sub indices for various pollutants for that sampling station is considered as AQI for that particular station. The respiratory parameter considered in this study was Forced Vital Capacity (FVC) and it was measured with the help of computerized Spirometer. Subjects having exposure to air pollution for duration of 1-5 years were selected for the study. Also control subjects were selected who were not exposed to air pollution but are of same socio-economic background for comparison purpose. Data related to cardiovascular risk including age, body mass index, weight and height, systolic and diastolic blood pressure was measured. Blood pressure was measured with the subject seated. Cigarette smoking, alcohol consumption, medical history including respiratory and cardiovascular conditions and subject’s use of medications were ascertained by questionnaire. As it is very difficult to calculate increase of blood pressure in absolute terms, Indices were developed for systolic blood pressure and diastolic blood pressure and are represented as ISBP and IDBP i.e. percentage increase in systolic blood pressure in fraction and percentage increase in diastolic blood pressure in fraction. The lung capacity of a person depends upon its age, height and weight, and the reduction of lung volume due to air pollution. Therefore, it is not possible to find out the generalised amount of volume reduction due to pollution. So index was developed to find out the extent of damage in terms of percentage of volume reduction in fraction (IFVC). Linear regression analyses were conducted to assess the association between increase in blood pressure and decrease in forced vital capacity of lungs due to air pollution. For the analysis the multiple logistic regression analysis in SPSS was used. IFVC, IDBP and ISBP were calculated from the equations1 to 3. Predicted values of FVC was calculated by ERS-93 equations which were inbuilt in spirometer and is named as FVCP.

IFVC =( FVCP-FVC) / FVCP IDBP = (DBP-80)/80 ISBP = (SBP -120)/ 120

Where: FVC: Measured Forced vital capacity of lungs DBP: Measured Diastolic blood pressure SBP : Measured Systolic blood pressure Table-1 AQI values at various sampling stations Sampling Stations NO.

Parameter SO2 (µg/m³)

NO2 (µg/m³)

PM10 (µg/m³)

CO (mg/m³)

AQI

1

9.64

29.82

138

0.64

125

2

7.62

34.56

226

1.09

184

3

9.47

38.60

85

0.85

85

4

5.58

19.82

106

0.59

104

5

8.77

31.28

286

0.86

236

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Suresh Kumar Singh et al., American International Journal of Research in Formal, Applied & Natural Sciences, 19(1), June-August 2017, pp. 07-12

Table-2 Mean value of indices for exposure duration 1-5 years Station NO. 1

AQI

Exposure Duration in years 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 Control population

85

2

104

3

125

4

184

5

236

6

IFVC 0.0592 0.0662 0.1431 0.2062 0.2512 0.0693 0.0971 0.1547 0.2406 0.2721 0.0623 0.1274 0.1946 0.2523 0.2936 0.1152 0.1567 0.2262 0.2652 0.3052 0.1783 0.2311 0.2471 0.3017 0.3092 0.0413

ISBP

IDBP

0.063 0.065 0.137 0.182 0.227 0.072 0.134 0.220 0.226 0.303 0.137 0.175 0.250 0.284 0.296 0.170 0.185 0.291 0.308 0.308 0.209 0.261 0.263 0.308 0.309 0.0468

0.021 0.034 0.114 0.169 0.182 0.036 0.080 0.131 0.182 0.222 0.058 0.138 0.183 0.197 0.223 0.104 0.151 0.185 0.200 0.231 0.176 0.211 0.215 0.216 0.229 0.0292

Concentration of various pollutants at five locations and corresponding AQI is given in table-1. Percentage reduction in FVC percentage increase in SBP / DBP in fraction is given in table-2. It is clear from the observations that if AQI is increasing , reduction in FVC is increasing and blood pressure is also increasing. Observations also indicates that if AQI is constant but exposure duration is increasing, reduction in FVC is increasing and blood pressure is also increasing. III. Analysis (a) Statistical Analysis: Statistical parameters and coefficients for statistical verification and to establish relationship between IFVC and IDBP/ ISBP are tabulated in table-3 & table-4 . F-test and t-test is also done to check the significance of independent parameters ( IFVC) on dependent parameter ( IDBP/ISBP) Table No. 3 Statistical Constants for IDBP Model Summary Model 1

R .960(a)

R Square .923

Adjusted R Square .919

Std. Error of the Estimate .01884

ANOVA

Regression Residual Total

Sum of Squares .097 .008 .105

Df 1

Mean Square .097 .000

23 24

F

Sig.

273.890

.000

t B

Sig. Std. Error .449 .000

Coefficients Unstandardized Coefficients B Std. Error (Constant) .007 .010 IFVC .768 .046 Note: Predictors: (Constant), IFVC Dependent Variable: IDBP Independent Variable: IFVC

Standardized Coefficients Beta

AIJRFANS 17- 303; Š 2017, AIJRFANS All Rights Reserved

.960

.770 16.550

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Suresh Kumar Singh et al., American International Journal of Research in Formal, Applied & Natural Sciences, 19(1), June-August 2017, pp. 07-12

F-Test: H0 : β1 = β2 = 0 against H1 : not all βk = 0 :(k = 1,2) Anova table gives the value of calculated 'F' = 273.89 and Fn-k-1, α = 4.2793( From standard tables) Hence FCAL > Fk, Fn-k-1, α Hence, reject H0 at α=0.05 level of significance , therefore significance of individual β’s be tested by 't' test t-Test H0 : βJ = 0 against H1 : βJ ≠ 0 ( for j=1 ) The calculated value for’t’ statistics for β1 t (for β1 ) = 16.550 The value of tn-k-1;α/2=2.069 The value of t is > tn-k-1;α/2 therefore reject H0 Hence β1≠0 Thus the estimated multiple regression analysis equation for IDBP can be expressed as IDBP = 0.768IFVC +0.007 Table No. 4 Statistical Constants for ISBP Model Summary Model 2

R .940

R Square .884

Adjusted R Square .879

Std. Error of the Estimate .02808

ANOVA

Regression Residual Total

Sum of Squares .138 .018 .156

Df 1

Mean Square .138 .001

23 24

F

Sig.

174.896

.000

t B

Sig. Std. Error .013 .000

Coefficients

(Constant) IFVC

Unstandardized Coefficients B Std. Error .039 .014 .915 .069

Standardized Coefficients Beta .940

2.683 13.225

Note: Predictors: (Constant), IFVC Dependent Variable: ISBP Independent Variable: IFVC

F-Test H1 : β1 against H1 : not all βk = 0 :(k = 1) Anova table gives the value of calculated 'F' = 174.896 and Fk, n-k-1,α = 4,2793 ( From standard tables) Hence FCAL > Fk, Fn-k-1, α Hence, reject H0 at α=0.05 level of significance , therefore significance of individual β’s be tested by 't' test t-Test H0 : βJ = 0 against H1 : βJ ≠ 0 ( for j=1 ) The calculated value for’t’ statistics for β1 t (for β1 ) = 13.225 The value of tn-k-1;α/2=2.069 The value of t is > tn-k-1;α/2 therefore reject H0 Hence β1≠0 Thus the estimated multiple regression analysis equation for ISBP can be expressed as ISBP = 0.915 IFVC+0.039 (b) Graphical Analysis: Statistical analysis and trends of calculated values of IFVC, IDBP and ISBP indicates that best fit curve is linear one. Graph-1 represents observed values and fitted values in

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Suresh Kumar Singh et al., American International Journal of Research in Formal, Applied & Natural Sciences, 19(1), June-August 2017, pp. 07-12

.2 .1 0

Fitted value

.3

.4

estimated relationship between ISBP and IFVC and shows that both values are lies within close limits. Similarly Graph-2 represents observed values and fitted values in estimated relationship between IDBP and IFVC and shows that both values are lies within close limits.

.05

.1

.15

.2

.25

.3

IFVC 95% CI ISBP

Fitted values

isbp = 0.915*ifvc + 0.039

0

.05

.1

.15

.2

.25

Graph-1

.05

.1

.15

.2

.25

.3

IFVC 95% CI IDBP

Fitted values

idbp = 0.768*ifvc + 0.007

Graph-2 Graphical and statistical analysis clearly indicates that reduction in FVC is associated with increase in SBP/DBP. Line of best fit clearly shows relationship between IFVC and IDBP/ISBP . Dots are scattered plot between actual values of IDBP/ISBP and IFVC to evaluate the departure of regressed value. Most of the actual values of IDBP/ISBP are in close range of fitted values as most of the dots are in the shaded regions which is the 95% confidence level IV. Conclusion It can be established from the findings of the study that increase in SBP and DBP due to urban air pollution is closely associated with reduction in FVC of lungs of persons and lower pulmonary functions have a higher risk for developing cardiovascular diseases including hypertension. It is clear from the statistical analysis that independent variable IFVC accounts for the variation in ISBP up to 88.4% and remaining 11.6% is due to other reasons. It also indicates that independent variable account IFVC accounts for the variation in IDBP up to 92.3% and remaining variation is due to other reasons. Further multiple regression analysis estimated equations for showing relationship of ISBP/IDBP with IFVC were developed. Hence it is clear that long exposure duration in urban pollution is not only affecting the respiratory tract but also increasing the blood pressure. Hence it is the time to develop a city in such a manner so that urban pollution cannot exceed any time from safe limits.

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Suresh Kumar Singh et al., American International Journal of Research in Formal, Applied & Natural Sciences, 19(1), June-August 2017, pp. 07-12

References [1] [2] [3] [4] [5] [6] [7] [8] [9] [10] [11] [12] [13] [14]

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