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Asthma and
Air Pollution

A guide for health professionals

Introduction 
Health effects of outdoor air pollution
Outdoor air pollutants
Health effects of indoor air pollution
Indoor air pollutants
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Appendices
Content created MAR 2005
Content updated MAR 2005

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NextBackAppendix 4 Exposure and respiratory outcomes

Australian studies on associations between exposure to NO2, ETS, formaldehyde and VOC and respiratory outcomes including asthma

Abbreviations & Glossary

FEV1 = Forced Expiratory Volume in 1 second
FVC = Forced Vital Capacity
NS = Not significant (p>0.05)
OR = Odds ratio

Authors
City/Years
Study
Exposures
Confounders
Outcome
Findings
Garrett et al 19981  Latrobe Valley, Victoria
1989
Longitudinal: 80 households with 148 children (53 asthmatics and 95 non-asthmatics); over a year Indoor NO2 levels Controlled: parental asthma, parental allergy,  child age, passive smoking and socio-economic status measured by house ownership Respiratory symptoms Nitrogen dioxide concentrations in the study houses were low, with a total of 10 samples exceeding 60 ppb (115 µg/m3).  The overall median level was 11.6 micrograms/m3 (6.0 ppb), ranging from < 0.7 to 246 micrograms/m3 (128 ppb). Major indoor nitrogen dioxide sources were: gas stoves, vented gas heaters, and smoking. Some 67% of variation in indoor nitrogen dioxide levels could be explained by presence of major sources, house age, and outdoor levels. Gas stoves were the main contributors.

 The presence of a gas stove significantly increased the likelihood of respiratory symptoms (odds ratio 2.2 [1.0-4.8]). However, neither of the other major nitrogen dioxide sources, gas heaters or smoking, were found to be significantly associated with respiratory symptoms. Nitrogen dioxide exposure was a marginal risk factor for respiratory symptoms. The interaction between atopy and gas stoves or NO2 exposure was NS. 


Pilotto et al 19972  ACT Longitudinal: 388 children aged 6-11 years; conducted in winter Indoor NO2 levels Controlled ??? Respiratory symptoms Exposure to NO2 at hourly peak levels of the order of > or = 80 ppb, compared with background levels of 20 ppb,  was associated with a significant increase in sore throat, colds and absences from school.

Smith et al 20003 Adelaide A longitudinal study over 6 weeks

Self-reported asthma (n=125)

Participants wore lapel badges that measured NO2 daily Controlled for other exposures Respiratory symptoms A significant interaction between NO2 and age was observed. In adults, exposure to NO2 was associated with cough with a 1 day lag (OR: 1.15, 95% CI: 1.01-1.31). Daily personal exposures to NO2 are associated with asthmatic symptoms in children.

Volkmer et al 19954 South Australia Cross sectional study
14,124 families with a child aged 4 years 3 months to 5 years. (represents 73% of the targeted State preschool population.)
parental smoking, type of fuel used for cooking and

heating and method used for home cooling

Controlled for other exposures, geographic location and SES Respiratory health Natural gas stove compared to an electric stove was significantly associated with increased prevalence rates for: (i) asthma (odds ratio [OR] 1.24); (ii) wheezing in the preceding 12 months (OR 1.16); excessive colds (OR 1.14); and hay fever (OR 1.13). The use of a unflued gas heater  compared to other forms of heating was significantly associated with increased prevalence rates for dry cough (OR 1.26), ever having wheezed

(OR 1.15) and wheezing in the preceding 12 months (OR 1.18). The use of a wood fire/heater compared to other forms of heating was significantly associated with a reduced prevalence rate for dry cough (OR 0.84) and ever having wheezed (OR 0.82).

Parental smoking was significantly associated with increased prevalence rates for bronchitis (OR 1.21) and ever having wheezed (OR 1.24).


Lewis et al 19985 Hunter and Illawarra regions of New South Wales A cross-sectional survey: 1993 

3023 children aged 8 to 10 years.

Out door pollutants, passive smoking at home,  gas heaters. Controlled for other exposures Respiratory symptoms  gas heating was associated with frequent wheeze.

Presence of an adult smoker in the home was associated with chest colds


 Reese et al6 WA Cross sectional study: 468 children (48 with bronchioloitis) Cotinine levels Controlled for confounders??? Bronchioloits Cotinine levels were higher in the group with bronhiolitis compared to children with non respiratory illness. Cotinine levels were  correlated with parents’ current smoking 

 Habby et al 19947 from two rural regions of NSW Cross sectional study: 2765 children Parental smoking Controlled for confounders ??? Respiratory         illness, lung function, BHR Passive smoking was associated with reduced FEV1, PEFR, and FEF25-75%.

Garrett et al 19981 Latrobe Valley, Victoria

1989

Longitudinal: 80 households with 148 children (53 asthmatics and 95 non-asthmatics); over a year Formaldehyde levels: in homes Controlled: parental asthma, parental allergy,

child age, passive smoking and socio-economic status measured by house ownership

Atopy and Respiratory symptoms The median indoor formaldehyde level was 15.8 microg/ m3 (12.6ppb), with a maximum of 139 microg/m3 (111 ppb).  Formaldehyde exposure was associated with atopy (OR=1.40 (0.98-2.00, 95% CI) with an increase in bedroom formaldehyde levels of 10 microg/m3).  Furthermore, more severe allergic sensitization was   demonstrated with increasing formaldehyde exposure. On the other hand, there was no significant increase in the adjusted risk of asthma or   respiratory symptoms with formaldehyde exposure. However, among children suffering from respiratory symptoms, more frequent symptoms were  noted in those exposed to higher formaldehyde

Franklin et al 20008 Perth,

Year?

Cross sectional: 224 healthy children

6 to 13 yr of age

Formaldehyde: in homes Controlled: atopy and other variables Lung function Exhaled NO There was no effect of formaldehyde levels on FVC or FEV1. There was, however, significantly higher levels of NO2 measured from children living in homes with average formaldehyde levels greater than 50 ppb (p = 0.02). Exhaled NO levels were 15.5 ppb

(10.5 to 22.9 ppb) for children from homes with formaldehyde concentrations  50 ppb and 8.7 ppb (7.9 to 9.6 ppb) for children from homes with formaldehyde concentrations < 50 ppb


Beach et al 19979 Melbourne Double blind cross over study; 17 asthmatics; VOC free paint Vs conventional paint VOC in paint Controlled for with in variation Respiratory symptoms, lung function airway responsiveness The new paint appears to be less likely to cause a worsening of respiratory symptoms than conventional acrylic paint, although this difference is not reflected in measurements of lung function or airway responsiveness.

References

1 Garrett, M.H., et al., Respiratory Symptoms in Children and Indoor Exposure to Nitrogen Dioxide and Gas Stoves. Am. J. Respir. Crit. Care Med., 1998. 158(3): p. 891-895.
2 Pilotto, L.S., et al., Respiratory effects associated with indoor nitrogen dioxide exposure in children. International Journal of Epidemiology., 1997. 26(4): p. 788-96.
3 Smith, B.J., et al., Health effects of daily indoor nitrogen dioxide exposure in people with asthma. Eur Respir J. 2000. 16(5): p. 879-85.
4 Volkmer, R.E., et al., The prevalence of respiratory symptoms in South Australian preschool children. II. Factors associated with indoor air quality. JPCH, 1995. 31(2): p. 116-20.
5 Lewis, P.R., et al., Outdoor air pollution and children's respiratory symptoms in the steel cities of New South Wales. MJA, 1998. 169: p. 459-463.
6 Reese, A.C., et al., Relationship between urinary cotinine level and diagnosis in children admitted to hospital. American Review of Respiratory Disease., 1992. 146(1): p. 66-70.
7 Haby, M.M., J.K. Peat, and A.J. Woolcock, Effect of passive smoking, asthma, and respiratory infection on lung function in Australian children. Pediatric Pulmonology., 1994. 18(5): p. 323-9.
8 Franklin, P., P. Dingle, and S. Stick, Raised Exhaled Nitric Oxide in Healthy Children Is Associated with Domestic Formaldehyde Levels. Am. J. Respir. Crit. Care Med., 2000. 161(5): p. 1757-1759.
9 Beach, J.R., et al., The effects on asthmatics of exposure to a conventional water-based and a volatile organic compound-free paint.   Eur Respir J, 1997. 10(3): p. 563-6.

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