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Int. J. Life. Sci. Scienti. Res., 2(5): 588-591 (ISSN: 2455-1716) Impact Factor 2.4 SEPTEMBER-2016
http://ijlssr.com Copyright © 2015-2016 International Journal of Life-Sciences Scientific Research Page 588
Evaluation of Pulmonary Function in Car Spray
Paint Sprayers
Sumit Arora1
, YogishTripathi1
, Varun Malhotra1
*, Rinku Garg1
, Neera Goel1
, Maroosha1
1
Department of Physiology, Santosh Medical College, Santosh University, Ghaziabad, India
*
Address for Correspondence: Dr. Varun Malhotra, Professor and Head of Department, Department of Physiology,
Santosh Medical College, Santosh University, Ghaziabad, India
Received: 23 June 2016/Revised: 18 July 2016/Accepted: 13 August 2016
ABSTRACT- Introduction: Pulmonary function tests have added in the early detection of pulmonary dysfunction in
patients considered to be normal on the basis of clinical and radiological examination. The present study was designed to
evaluate pulmonary functions in car paint sprayers.
Material and Methods: Sixty subjects in the age group 18 to 45 year were divided into two groups (each group having
thirty subjects). Group A consisted of healthy controls. Group B consist of healthy, car paint sprayers. Car paint sprayers
had employment duration of 5 to 12 years. Anthropometric and respiratory parameters using MEBISOFT were performed.
Statistical analysis was performed using the Statistical Package for Social Sciences (SPSS‑17).
Results: The results of present study suggested that the values of FVC, FEV1, FEV1/FVC and PEFR were significantly
lower in subjects who were in Group B exposed to organic solvents (used for spraying car painting) when compared with
Group A subjects.
Conclusion: The present study results strongly recommend for following appropriate safety measure while spraying car
painting using organic solvents irrespective of their smoking status and age.
Key-words: Pulmonary function, Car spray painters, SPSS‑17, Anthropometry, BSA, FVC
-------------------------------------------------IJLSSR-----------------------------------------------
INTRODUCTION
Pulmonary function tests have added in the early detection
of pulmonary dysfunction in patients considered to be
normal on the basis of clinical and radiological
examination.Car paint sprayers are exposed to
iso-cyanates1
which are a group of low molecular weight
aromatic and aliphatic compounds containing the highly
reactive isocyanate group (-NCO)2
. The most commonly
used isocyanates include toluene di isocyanate (TDI),
diphenyl methane di isocyanate (MDI), hexamethylene di
isocyanate (HDI), and biuret modified HDI (HDI-BT)3
.
Most of the isocyanate compounds are colorless, yellow, or
brown liquids with sharp pungent odours. Inhalation and
dermal exposure can occur during the manufacture and use
of these compounds.
Access this article online
Quick Response Code:
Website:
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DOI:
10.21276/ijlssr.2016.2.5.13
Isocyanates are used as cross-linking agents in
polyurethane products such as foams, varnishes, and paints.
Therefore, workers and individuals in close proximity to
spray application of polyurethane are very likely to be
exposed 4
.
Chronic inhalation can cause immune disorders as well as
nasal and lung lesions. Chronic inhalational exposure to
isocyanates in plant workers has been linked to pulmonary
effects that are characterized by dyspnoea, wheezing and
bronchial constriction5
. Detailed medical and occupational
history should be obtained to investigate the relationship
between asthmatics symptoms and workplace exposure6
.
In addition, different types of pulmonary function and
inhalation challenge tests are used to confirm diagnosis of
Occupational asthma. However, since repeated pulmonary
function testing is not sufficient to diagnose and evaluate
pulmonary damage induced by car paint sprays3
, low
molecular weight proteins were introduced as interesting
peripheral biomarkers.6-11
MATERIALS AND METHODS
Sixty subjects in the age group 18 to 45 year were divided
into two groups (each group having thirty subjects).
Group A consisted of healthy controls. Group B consist of
healthy, car paint sprayers. Car paint sprayers had
Research Article (Open access)
Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 5
http://ijlssr.com Copyright © 2015-2016 International Journal of Life-Sciences Scientific Research Page 589
employment duration of 5 to 12 years.
The study was conducted in Department of Physiology,
Santosh Medical College, Ghaziabad, India & Sudhanshu
Automobile Company in Delhi, India. A written consent
was taken from them. Subjects with FEV1% value less
than 60% of predicted value was excluded from the study.
The subjects of both group had no present or past history
of recurrent respiratory infection, cough or dyspnea. They
were non-smokers. There was no clinical evidence of
malnutrition, heart disease or any other physical ailment.
The following measurement was carried out on each
subject:
Anthropometry: Height and weight was measured.
Body surface Area (BSA): in square meters was
calculated from the height and weight of the subject using
Du-Bois normogram.
Respiratory parameters: Respiratory parameters by
spirometry. At least three acceptable and reproducible
Maximal Expiratory Flow volume (MEFV) Curves were
obtained after explaining the procedure. They were
monitored on the computer screen. In the present study all
the parameters were studied by using MEBISOFT. The
highest FEVI from the best three curves were selected for
assessment and following parameters were computed FVC
(Forced Vital Capacity), FEVI (Forced Expiratory Volume
in First Second), FEV,/FVC, FEF25_75 (Forced
Expiratory Flow at 25% - 75%), PEFR (Peak Expiratory
Flow Rate), FEF50 (Forced Expiratory Flow at 50% of
FVC), MVV (Maximum Voluntary Ventilation) , FRC
(Functional Residual Capacity), RV (Residual Volume),
TLC (Total Lung Capacity), DLCO (Carbon Monoxide
Diffusion Capacity)
Statistical analysis was performed using the Statistical
Package for Social Sciences (SPSS‑17). The results were
expressed as mean ± standard deviation (SD). Independent
t-test was applied to study the PFTs in smokers and
non‑smokers and also for worker with symptoms
suggestive of Occupational Asthma and without
Occupational Asthma. Relationship between duration of
exposure and respiratory morbidity state was studied by
correlation test. P < 0.05 was considered significant.
RESULTS
Comparison of anthropometric parameters (Body surface
area [BSA], weight and height) among Group A and
Group B subjects is shown in Table 1.
There was no statistical difference in body surface area
and height between Group A and Group B subjects. The
mean weight of subjects of Group B group (63 Kg) was
less than the subjects of Group A groups (72 Kg) with
mean difference of 9 kg. Overall, the anthropometric
parameters were similar in both the groups.
Table 1: Comparison of anthropometric parameters
among Group A and Group B subjects
Parameter
Group A
N = 30
Group B
N = 30
Body surface area 1.76±0.14 1.64±0.09 NS
Height 1.56±0.11 1.54 ±0.07 NS
Weight 71.74±9.97 63.20±6.73 NS
Values are expressed as Mean ±SD
N: Number of subject in each group
NS: Not Significant
Group A: Unexposed Worker
Group B: Exposed Worker
Table 2: Comparison of Pulmonary Function
parameters among Group A and Group B subjects
Group A
N = 30
Mean ±SD
Group B
N = 30
Mean±SD
P-value
Forced Vital
Capacity (L)
2.99±0.14 2.36±0.30 P< 0.001
Forced Expiratory
Volume in FIRST
second (L/sec)
2.84±0.15 1.75±0.31 P< 0.001
Ratio of FEV1 to
FVC
95.08±2.17 74.48±12.65 P< 0.001
Forced Expiratory
Flow over 25% to
75% of FVC
3.34 ± 0.19 2.21±0.43 P< 0.001
Peak Expiratory
Flow Rate (L/sec)
7.86±2.08 4.55±0.40 P< 0.001
Forced Expiratory
Flow at 505 of FVC
(L/sec)
4.55±0.19 3.24±0.82 P< 0.001
Maximum
Voluntary
Ventilation (L/min)
107.63±5.43 85.62±19.93 P< 0.001
Residual volume (L) 1.63±0.19 1.16± 0.40 P< 0.001
Total lung capacity
(L)
4.74±0.51 3.14± 1.11 P< 0.001
Carbon Monoxide
Diffusion Capacity
28.10±0.57 23.20±4.27 P< 0.001
Values are expressed as Mean (±SD)
N= Number of subject in each group
Group a: Unexposed Worker
Group b: Exposed Worker P< 0.001
Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 5
http://ijlssr.com Copyright © 2015-2016 International Journal of Life-Sciences Scientific Research Page 590
The results of present study suggested that the values of
FVC, FEV1, FEV1/FVC and PEF were significantly lower
in subjects who were in Group B to organic solvents (used
for spraying car painting) when compared with Group A
subjects (Table 1). The difference in PFT markers between
both Group B and Group A was statistically significant.
The other pulmonary impairment parameters included
forced expiratory flow over 25% to 75% of FVC, forced
expiratory flow at 505 of FVC, maximum voluntary
ventilation and residual volume. In addition, total lung
capacity (L) and carbon monoxide diffusion capacity
significantly decreased in Group B subject than Group A
subjects. There was statistical significant difference in all
pulmonary function parameters compared between Group
B and Group A subjects. These results suggest that the
changes in pulmonary function in Group B subject were
due to organic solvent which is used for spraying car
painting.
DISCUSSION
In the present study, the pulmonary function markers of
subjects who were exposed to car painting vapors
significantly decreased compared with unexposed subject,
indicating that the pulmonary function impairment in
exposed subject was due to organic solvent which was used
for spraying car painting.
The present study, all the key pulmonary function
parameters including total lung capacity and carbon
monoxide diffusion capacity were significantly lower in
exposed subject than unexposed subjects.
Wink12
showed that mean peak flow in workers decreased
significantly on the day of exposure and increased on days
when the workers were stayed away from work.
In other study, significantly lower FVC, FEV1 and
FEF25-75% values were recorded in both higher and lower
age group smokers and non-smokers paint workers in
comparison to control group except FEV1% and PEFR
values of higher age group paint workers, where it showed
significantly lower values than control group workers.13
Again, Saad14
studied on tannery workers exposed to
benzene and formaldehyde and found that the values of
pulmonary function parameters (FVC, FEV1) were
significantly lower in the exposed workers.
Metwally13
explained these findings by longer duration of
exposure and older age with high solvent exposed group of
workers resulting in further deterioration in lung function
parameters. These results corroborated with the study of
Schweigert.14
who studied car paint sprayers exposed to
solvent. They found that there was progressive decline in
percentage of predicted FEV1 with increasing intensity of
solvent exposure.
Chattopadhyay Parkar15
and Cullen16
pointed out that
obstructive impairment was more frequent in smoker
workers but increased frequency of restrictive impairment
was not statistically significant with smoking which
corroborated with our findings.
Metwally13
and Dement17
demonstrated increased risk of
COPD among paint workers exposed to solvent, which was
in accordance with our findings where prevalence of chest
tightness, chronic Bronchitis and Bronchial asthma was
high among high Volatile organic compounds exposed
paint workers in comparison to low VOC exposed group.
These respiratory effects were probably due to Volatile
organic compounds, and Xylene induced oxidative stress.18s
Other results suggested that the decrease in forced vital
capacity might serve as a guide to identify car painters at
risk of a further decrement in lung function.19
In this
respect, many researchers indicated that exposure to low
toluene disocyanate concentrations was associated with
minimal but detectable changes in airway caliber and in
epithelial barrier permeability causing some changes in the
pulmonary function,20
and nearly 36.4% of the car paint
sprayers had some form of pulmonary function impairment;
obstructive and/or restrictive 21-22.
In our study, the correlation between pulmonary function
parameters with duration of exposure to painting solvents
and age of car paint sprayers (years) was negative except
for forced expiratory flow at 505 of FVC and carbon
monoxide diffusion capacity.
It has been reported that the car painters who smoke less
are less likely to use respiratory protection in highly
exposed situations and therefore show a greater decline in
lung function.
CONCLUSION
The present study results recommends for following
appropriate safety measure while spraying car painting
using organic solvents irrespective of their smoking status
and age; however it is highly recommended to the subjects
who are chronic smokers. The smoking populations of
workers who ignore to follow standard protection measures
during car painting are at very high risk of developing
pulmonary impairment. Exposure to paints leads to an
obstructive pattern of impairment of pulmonary function.
ACKNOWLEDGMENT
The present study results recommends for following
appropriate safety measure while spraying car painting
using organic solvents irrespective of their smoking status
and age; however it is highly recommended to the subjects
who are chronic smokers. The smoking populations of
workers who ignore to follow standard protection measures
during car painting are at very high risk of developing
pulmonary impairment. Exposure to paints leads to an
obstructive pattern of impairment of pulmonary function.
REFERENCES
[1] Alexenderson, R; Hedensteirna, G.; Plato, N. and
Kolmodin-Hedman, B. “Exposure, lung function, and
symptoms in car painters exposed to hexa methylene di
isocyanate and biuret modified hexa methylene di
isocyanate”. Arch. Environ. Health, 1987:42:367-373.
Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 5
http://ijlssr.com Copyright © 2015-2016 International Journal of Life-Sciences Scientific Research Page 591
[2] Schauerte, K.; Dahm, M.; Diller, W. And Uhlig, K.
Sonderdruckaus “Occupational asthma and extrinsic
alveoloitis due to isocyanates: current status and
perspectives”. Br. J. Ind. Med., 1985: 50:213-228.
[3] Vandenplas, O.; Malo, J. L.; Saetta, M.; Mapp, C. E. and
Fabbri, L. M. Poly isocyanates and their prepolymers. In:
Asthma in the Workplace and Related Conditions.
Bernstein 1993 I. L.;
[4] Pronk, A.; Preller, L.; Raulf-Heimsoth, M.; Jonkers, I. M.;
Doekes, G; Wisnewski, A. V. and HEEDERIK, D.
“Respiratory symptoms and sensitization, and exposure
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isocyanates”. Am. J. Respir. Crit. Care. Med., 176:
1090-1097.
[5] Mapp, C. E.; Polato, R.; Mastrelli, P.; Hendrick, D. J. And
Fabbri, L. M. “Time course of the increase in airway
responsiveness associated with late asthmatic reactions to
toluene di isocyanate in sensitized subjects”. Allergy Clin.
Immunol., 1985, 75: 568-572.
[6] Malo, J-L; Lemière, C; Gautrin, D; Labrecque, M.
Occupational asthma. Curr Opin Pulm Med 2004, 10,
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[7] Kumar V, Abbas AK, Fausto N, Mitchell RN Robbins Basic
Pathology (8th
Ed.) Sounders Elsevier 2007, 516-522.
[8] Wedeen RP. Renal diseases of occupational origin. Occup
Med 1992; 7:449–63.
[9] Lundberg I, and Hakansoon M. Normal serum activities of
liver enzymes in Swedish paint industry workers with heavy
exposure to organic solvents. Br J Indust Med 1985; 42:
596-600.
[10]Mohammadi S, Mehrparvar A, Labbafinejad Y, and Attarchi
MS. The effect of exposure to a mixture of organic solvents
on liver enzymes in an auto manufacturing plant. J Public
Health 2010; 18:553-557.
[11]Parker DL, Waller K, Himrich B, Martinez A, and Martin F.
A Cross-sectional study of pulmonary function in auto body
repair workers. Am J Public Health 1991; 81(6):768-771.
[12]Trzcinka-Ochocka M, Jakubowski M, Hałatek T,
Raźniewska G. Reversibility of proteinuria in
nickel-cadmium battery workers after removal from
exposure. Int Arch Occup Environ Health 2002; 75 (Suppl):
S101–6.
[13]Metwally FM, Hafez SF, Abd EI Gawad NB, Saeed KM.
Respiratory manifestations in Workers Occupationally
Exposed to organic Solvents. Journal of Applied Sciences
Research. 2012; 8(12):5736-5743
[14]Saad A, Hammad S, Amir N, Rashad H, Mohamed K.
Cytogenetic study on tannery workers and the synergistic
role of smoking. CentrEur J OccupEnviron Med. 2008,
14(3): 239-41. Compounds emitted from water based Paints.
J Occup. Environ Med. 2007;49(8):880-9.
[15]Gee JB, Morgan WK. A 10-year follow up study of a group
of workers exposed to Isocyanate. J Occup Med. 1985;
34(1):263-71.
[16]Cullen MR, Redlich CA, Beckett WS, Weltmann B, Sparer
J, Jackson G, Ruff T, Rubinstein E, Holden W. Feasibility
study of respiratory questionnaire and peak flow recordings
in autobody shop workers exposed to isocyanate-containing
spray paint: Observations and limitations. Occup Med (Lond)
1996; 46(3):197-204.
[17] Aggarwal AN, Gupta D, Behera D, Jindal SK. Applicability
of commonly used Caucasian prediction equations for
spirometry interpretation in India. Indian J Med Res.
2005,122 (2):93-186.
[18]Dement JM, Welch L, Ringen K, Bingham E, Quinn P.
Airways obstruction among older construction and trade
workers. Am J Ind Med. 2010; 53(3):224-40.
[19]Taylor SA, Chivers ID, Price RG. The assessment of
biomarkers to detect nephrotoxicity using an integrated
database. Environ Res 1997; 75:23–33.
[20]David NJ, Wolman R, Milne FJ, Van Niekerk I. Acute renal
failuredue to trichloroethylene poisoning. Brit J Ind Med
1989; 46:347–9.
[21]Snyder R, editor. Ethel Browning’s Toxicity and Metabolism
of Industrial Solvents. 2nd ed. Amsterdam: Elsevier Science
Publishers; 1987.
[22]Beirne GJ, Brennan JT. Glomerulo nephritis associated with
hydrocarbonsolvents mediated by antiglomerular basement
membrane antibody. Arch Environ Health 1972; 25:365–9.
Source of Financial Support: Nil
Conflict of interest: Nil
International Journal of Life-Sciences Scientific Research (IJLSSR)
Open Access Policy
Authors/Contributors are responsible for originality, contents, correct
references, and ethical issues.
IJLSSR publishes all articles under Creative Commons Attribution-
Non-Commercial 4.0 International License (CC BY-NC).
https://creativecommons.org/licenses/by-nc/4.0/

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Evaluation of Pulmonary Function in Car Spray Paint Sprayers

  • 1. Int. J. Life. Sci. Scienti. Res., 2(5): 588-591 (ISSN: 2455-1716) Impact Factor 2.4 SEPTEMBER-2016 http://ijlssr.com Copyright © 2015-2016 International Journal of Life-Sciences Scientific Research Page 588 Evaluation of Pulmonary Function in Car Spray Paint Sprayers Sumit Arora1 , YogishTripathi1 , Varun Malhotra1 *, Rinku Garg1 , Neera Goel1 , Maroosha1 1 Department of Physiology, Santosh Medical College, Santosh University, Ghaziabad, India * Address for Correspondence: Dr. Varun Malhotra, Professor and Head of Department, Department of Physiology, Santosh Medical College, Santosh University, Ghaziabad, India Received: 23 June 2016/Revised: 18 July 2016/Accepted: 13 August 2016 ABSTRACT- Introduction: Pulmonary function tests have added in the early detection of pulmonary dysfunction in patients considered to be normal on the basis of clinical and radiological examination. The present study was designed to evaluate pulmonary functions in car paint sprayers. Material and Methods: Sixty subjects in the age group 18 to 45 year were divided into two groups (each group having thirty subjects). Group A consisted of healthy controls. Group B consist of healthy, car paint sprayers. Car paint sprayers had employment duration of 5 to 12 years. Anthropometric and respiratory parameters using MEBISOFT were performed. Statistical analysis was performed using the Statistical Package for Social Sciences (SPSS‑17). Results: The results of present study suggested that the values of FVC, FEV1, FEV1/FVC and PEFR were significantly lower in subjects who were in Group B exposed to organic solvents (used for spraying car painting) when compared with Group A subjects. Conclusion: The present study results strongly recommend for following appropriate safety measure while spraying car painting using organic solvents irrespective of their smoking status and age. Key-words: Pulmonary function, Car spray painters, SPSS‑17, Anthropometry, BSA, FVC -------------------------------------------------IJLSSR----------------------------------------------- INTRODUCTION Pulmonary function tests have added in the early detection of pulmonary dysfunction in patients considered to be normal on the basis of clinical and radiological examination.Car paint sprayers are exposed to iso-cyanates1 which are a group of low molecular weight aromatic and aliphatic compounds containing the highly reactive isocyanate group (-NCO)2 . The most commonly used isocyanates include toluene di isocyanate (TDI), diphenyl methane di isocyanate (MDI), hexamethylene di isocyanate (HDI), and biuret modified HDI (HDI-BT)3 . Most of the isocyanate compounds are colorless, yellow, or brown liquids with sharp pungent odours. Inhalation and dermal exposure can occur during the manufacture and use of these compounds. Access this article online Quick Response Code: Website: www.ijlssr.com DOI: 10.21276/ijlssr.2016.2.5.13 Isocyanates are used as cross-linking agents in polyurethane products such as foams, varnishes, and paints. Therefore, workers and individuals in close proximity to spray application of polyurethane are very likely to be exposed 4 . Chronic inhalation can cause immune disorders as well as nasal and lung lesions. Chronic inhalational exposure to isocyanates in plant workers has been linked to pulmonary effects that are characterized by dyspnoea, wheezing and bronchial constriction5 . Detailed medical and occupational history should be obtained to investigate the relationship between asthmatics symptoms and workplace exposure6 . In addition, different types of pulmonary function and inhalation challenge tests are used to confirm diagnosis of Occupational asthma. However, since repeated pulmonary function testing is not sufficient to diagnose and evaluate pulmonary damage induced by car paint sprays3 , low molecular weight proteins were introduced as interesting peripheral biomarkers.6-11 MATERIALS AND METHODS Sixty subjects in the age group 18 to 45 year were divided into two groups (each group having thirty subjects). Group A consisted of healthy controls. Group B consist of healthy, car paint sprayers. Car paint sprayers had Research Article (Open access)
  • 2. Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 5 http://ijlssr.com Copyright © 2015-2016 International Journal of Life-Sciences Scientific Research Page 589 employment duration of 5 to 12 years. The study was conducted in Department of Physiology, Santosh Medical College, Ghaziabad, India & Sudhanshu Automobile Company in Delhi, India. A written consent was taken from them. Subjects with FEV1% value less than 60% of predicted value was excluded from the study. The subjects of both group had no present or past history of recurrent respiratory infection, cough or dyspnea. They were non-smokers. There was no clinical evidence of malnutrition, heart disease or any other physical ailment. The following measurement was carried out on each subject: Anthropometry: Height and weight was measured. Body surface Area (BSA): in square meters was calculated from the height and weight of the subject using Du-Bois normogram. Respiratory parameters: Respiratory parameters by spirometry. At least three acceptable and reproducible Maximal Expiratory Flow volume (MEFV) Curves were obtained after explaining the procedure. They were monitored on the computer screen. In the present study all the parameters were studied by using MEBISOFT. The highest FEVI from the best three curves were selected for assessment and following parameters were computed FVC (Forced Vital Capacity), FEVI (Forced Expiratory Volume in First Second), FEV,/FVC, FEF25_75 (Forced Expiratory Flow at 25% - 75%), PEFR (Peak Expiratory Flow Rate), FEF50 (Forced Expiratory Flow at 50% of FVC), MVV (Maximum Voluntary Ventilation) , FRC (Functional Residual Capacity), RV (Residual Volume), TLC (Total Lung Capacity), DLCO (Carbon Monoxide Diffusion Capacity) Statistical analysis was performed using the Statistical Package for Social Sciences (SPSS‑17). The results were expressed as mean ± standard deviation (SD). Independent t-test was applied to study the PFTs in smokers and non‑smokers and also for worker with symptoms suggestive of Occupational Asthma and without Occupational Asthma. Relationship between duration of exposure and respiratory morbidity state was studied by correlation test. P < 0.05 was considered significant. RESULTS Comparison of anthropometric parameters (Body surface area [BSA], weight and height) among Group A and Group B subjects is shown in Table 1. There was no statistical difference in body surface area and height between Group A and Group B subjects. The mean weight of subjects of Group B group (63 Kg) was less than the subjects of Group A groups (72 Kg) with mean difference of 9 kg. Overall, the anthropometric parameters were similar in both the groups. Table 1: Comparison of anthropometric parameters among Group A and Group B subjects Parameter Group A N = 30 Group B N = 30 Body surface area 1.76±0.14 1.64±0.09 NS Height 1.56±0.11 1.54 ±0.07 NS Weight 71.74±9.97 63.20±6.73 NS Values are expressed as Mean ±SD N: Number of subject in each group NS: Not Significant Group A: Unexposed Worker Group B: Exposed Worker Table 2: Comparison of Pulmonary Function parameters among Group A and Group B subjects Group A N = 30 Mean ±SD Group B N = 30 Mean±SD P-value Forced Vital Capacity (L) 2.99±0.14 2.36±0.30 P< 0.001 Forced Expiratory Volume in FIRST second (L/sec) 2.84±0.15 1.75±0.31 P< 0.001 Ratio of FEV1 to FVC 95.08±2.17 74.48±12.65 P< 0.001 Forced Expiratory Flow over 25% to 75% of FVC 3.34 ± 0.19 2.21±0.43 P< 0.001 Peak Expiratory Flow Rate (L/sec) 7.86±2.08 4.55±0.40 P< 0.001 Forced Expiratory Flow at 505 of FVC (L/sec) 4.55±0.19 3.24±0.82 P< 0.001 Maximum Voluntary Ventilation (L/min) 107.63±5.43 85.62±19.93 P< 0.001 Residual volume (L) 1.63±0.19 1.16± 0.40 P< 0.001 Total lung capacity (L) 4.74±0.51 3.14± 1.11 P< 0.001 Carbon Monoxide Diffusion Capacity 28.10±0.57 23.20±4.27 P< 0.001 Values are expressed as Mean (±SD) N= Number of subject in each group Group a: Unexposed Worker Group b: Exposed Worker P< 0.001
  • 3. Int. J. Life. Sci. Scienti. Res., VOL 2, ISSUE 5 http://ijlssr.com Copyright © 2015-2016 International Journal of Life-Sciences Scientific Research Page 590 The results of present study suggested that the values of FVC, FEV1, FEV1/FVC and PEF were significantly lower in subjects who were in Group B to organic solvents (used for spraying car painting) when compared with Group A subjects (Table 1). The difference in PFT markers between both Group B and Group A was statistically significant. The other pulmonary impairment parameters included forced expiratory flow over 25% to 75% of FVC, forced expiratory flow at 505 of FVC, maximum voluntary ventilation and residual volume. In addition, total lung capacity (L) and carbon monoxide diffusion capacity significantly decreased in Group B subject than Group A subjects. There was statistical significant difference in all pulmonary function parameters compared between Group B and Group A subjects. These results suggest that the changes in pulmonary function in Group B subject were due to organic solvent which is used for spraying car painting. DISCUSSION In the present study, the pulmonary function markers of subjects who were exposed to car painting vapors significantly decreased compared with unexposed subject, indicating that the pulmonary function impairment in exposed subject was due to organic solvent which was used for spraying car painting. The present study, all the key pulmonary function parameters including total lung capacity and carbon monoxide diffusion capacity were significantly lower in exposed subject than unexposed subjects. Wink12 showed that mean peak flow in workers decreased significantly on the day of exposure and increased on days when the workers were stayed away from work. In other study, significantly lower FVC, FEV1 and FEF25-75% values were recorded in both higher and lower age group smokers and non-smokers paint workers in comparison to control group except FEV1% and PEFR values of higher age group paint workers, where it showed significantly lower values than control group workers.13 Again, Saad14 studied on tannery workers exposed to benzene and formaldehyde and found that the values of pulmonary function parameters (FVC, FEV1) were significantly lower in the exposed workers. Metwally13 explained these findings by longer duration of exposure and older age with high solvent exposed group of workers resulting in further deterioration in lung function parameters. These results corroborated with the study of Schweigert.14 who studied car paint sprayers exposed to solvent. They found that there was progressive decline in percentage of predicted FEV1 with increasing intensity of solvent exposure. Chattopadhyay Parkar15 and Cullen16 pointed out that obstructive impairment was more frequent in smoker workers but increased frequency of restrictive impairment was not statistically significant with smoking which corroborated with our findings. Metwally13 and Dement17 demonstrated increased risk of COPD among paint workers exposed to solvent, which was in accordance with our findings where prevalence of chest tightness, chronic Bronchitis and Bronchial asthma was high among high Volatile organic compounds exposed paint workers in comparison to low VOC exposed group. These respiratory effects were probably due to Volatile organic compounds, and Xylene induced oxidative stress.18s Other results suggested that the decrease in forced vital capacity might serve as a guide to identify car painters at risk of a further decrement in lung function.19 In this respect, many researchers indicated that exposure to low toluene disocyanate concentrations was associated with minimal but detectable changes in airway caliber and in epithelial barrier permeability causing some changes in the pulmonary function,20 and nearly 36.4% of the car paint sprayers had some form of pulmonary function impairment; obstructive and/or restrictive 21-22. In our study, the correlation between pulmonary function parameters with duration of exposure to painting solvents and age of car paint sprayers (years) was negative except for forced expiratory flow at 505 of FVC and carbon monoxide diffusion capacity. It has been reported that the car painters who smoke less are less likely to use respiratory protection in highly exposed situations and therefore show a greater decline in lung function. CONCLUSION The present study results recommends for following appropriate safety measure while spraying car painting using organic solvents irrespective of their smoking status and age; however it is highly recommended to the subjects who are chronic smokers. The smoking populations of workers who ignore to follow standard protection measures during car painting are at very high risk of developing pulmonary impairment. Exposure to paints leads to an obstructive pattern of impairment of pulmonary function. ACKNOWLEDGMENT The present study results recommends for following appropriate safety measure while spraying car painting using organic solvents irrespective of their smoking status and age; however it is highly recommended to the subjects who are chronic smokers. The smoking populations of workers who ignore to follow standard protection measures during car painting are at very high risk of developing pulmonary impairment. Exposure to paints leads to an obstructive pattern of impairment of pulmonary function. REFERENCES [1] Alexenderson, R; Hedensteirna, G.; Plato, N. and Kolmodin-Hedman, B. “Exposure, lung function, and symptoms in car painters exposed to hexa methylene di isocyanate and biuret modified hexa methylene di isocyanate”. Arch. Environ. Health, 1987:42:367-373.
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