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Eur Respir J 2001; 17:604-608
Copyright ©ERS Journals Ltd 2001

The effect of sulphur dioxide exposure on indices of heart rate variability in normal and asthmatic adults

W.S. Tunnicliffe1, M.F. Hilton1, R.M. Harrison2 and J.G. Ayres1

1 Heartlands Research Institute, Heartlands Hospital, Bordesley Green East, Birmingham, UK. 2 Division of Environmental Health & Risk Management, University of Birmingham, Edgbaston, Birmingham, UK

CORRESPONDENCE: J.G. Ayres, Heartlands Research Institute, Heartlands Hospital, Bordesley Green East, B9 5SS, Birmingham, UK. Fax: 44 1217724259

Keywords: air pollution, health effects, heart rate variability, mechanisms, sulphur dioxide

Received: March 10, 2000
Accepted December 18, 2000


   Abstract
TOP
 Abstract
Subjects and methods
 Results
 Discussion
 References
 
Sulphur dioxide (SO2) is an important air pollutant and causes bronchoconstriction in normal and asthmatic adults. This paper has explored the autonomic consequences of SO2 exposure using the spectral analysis of heart rate variability.

Electrocardiogram recordings were made in 12 normal and 12 asthmatic adults undergoing pollutant exposures. Exposures were of a 1 h duration, double blind, in random order, ≥2 weeks apart and included air and 200 parts per billion SO2. Spectral analysis of R-R intervals was performed.

SO2 exposure was associated with an increase in total power (TP) and high (HF) and low frequency (LF) power in the normal subjects, and a reduction in these indices in the subjects with asthma. The difference in TP with SO2 exposure compared to air was +1730 ms2 in the normal group and –1021 ms2 asthmatic group (p<0.003). For HF the respective values were +964 ms2 and –539 ms2 (p=0.02) and for LF, +43 7 ms2 and –57 2 ms2 (p=0.01). No change in lung function or symptoms was observed in either group.

This suggests that SO2 exposure at concentrations which are frequently encountered during air pollution episodes can influence the autonomic nervous system. This may be important in understanding the mechanisms involved in SO2 induced bronchoconstriction, and of the cardiovascular effects of air pollution.

Sulphur dioxide (SO2) is a common outdoor air pollutant and is associated with day to day changes in hospitalization rates for lung disease in Europe 1. While annual mean concentrations in urban areas of the UK are generally in the range of 10–20 parts per billion (ppb), maximum 1-h means of 200–300 ppb are commonly recorded. Recently, maximum 1-h means >500 ppb were recorded in Belfast. These concentrations are commonly exceeded in Eastern Europe 2.

In challenge studies, SO2 is capable of producing bronchoconstriction in both normal and asthmatic subjects 3. Normal subjects vary considerably in their response to this gas, most responding to concentrations of 4,000–5,000 ppb 4, but no effects have been recorded in normal individuals exposed to concentrations <1,000 ppb 5. Bronchoconstriction in asthmatic subjects occurs at lower concentrations, changes in lung function being detectable at concentrations of 400 ppb when exposures are combined with exercise 5. The mechanisms producing bronchoconstriction in humans are relatively poorly understood, but are thought to involve stimulation of irritant receptors in the upper airway 6. Atropine has been shown to block SO2 induced bronchoconstriction in normal adults 7, suggesting a cholinergic reflex, but this agent is only partially effective in subjects with asthma 8. Neither the difference in the sensitivity between asthmatics and normals to SO2, nor the differing effects of atropine blockade in these groups have been adequately explained. This questioned whether these observed differences might be explained by differing autonomic responses of these groups to SO2 exposure.

Spectral analysis of heart rate variability (HRV) is now an established clinical and research tool for the noninvasive assessment of autonomic nervous system function in humans 9. In brief, a continuous electrocardiogram (ECG) is recorded for off-line computer analysis. The recording is edited to remove nonsinus ectopic beats, pauses, artefacts and nonperiodic R-R interval (the time between successive ventricular depolarizations) changes. The R-R intervals are then measured and power spectral density analysis is performed to give information about how power (variance) distributes as a function of frequency. In short-term recordings, three main spectral components are distinguishable; very low frequency (VLF) (≤0.04 Hz), low frequency (LF) (0.04–0.15 Hz) and high frequency (HF) (0.15–0.4 Hz). In addition, total power (TP) is measured as a sum of these components. The physiological explanation of the VLF component is poorly defined; in contrast, the LF component is recognized as chiefly reflecting sympathetic modulation while the HF component reflects almost exclusively parasympathetic (vagal) modulation. Relative sympathetic and parasympathetic balance is reflected in the LF:HF ratio 9.

As part of a series of studies of the effects of pollutant exposures in males, the autonomic consequences of exposure to 200 ppb SO2 in normal and asthmatic adult volunteers was explored. The intention was to determine whether an air pollutant exposure at a relevant concentration might be associated with a detectable change in autonomic nervous system modulation and if so, to characterize the nature of the response in normal and asthmatic subjects.


   Subjects and methods
TOP
 Abstract
 Subjects and methods
Results
 Discussion
 References
 
Subjects
Twenty-four adult volunteers participating in a study of the respiratory effects of exposure to fine particulate sulphuric acid and ammonium bisulphate, and to SO2 were studied. Half of the subjects had physician diagnosed mild asthma, the others were normal, healthy adults (table 1Go). None of the volunteers were current smokers and subjects with coexisting cardiovascular disease or who were using cardiovascular medication were excluded. The asthmatic subjects were using only short acting ß-agonists with or without inhaled corticosteroids at a dose not exceeding 400 µg of beclomethasone or equivalent, per day. All users of ß-agonists were required to refrain from their use for a minimum of 4 h before undergoing each pollutant exposure. The project was approved by the East Birmingham Health Authority research and ethics committee.


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  		Table 1 Characteristics of study groups

 
Exposures
Exposures were ≥2 weeks apart, of 1-h duration at rest and were conducted at the same time of the day for each individual. The pollutants used were 200 ppb SO2, and two doses each of particulate ammonium bisulphate and sulphuric acid; only the results following SO2 are presented here. Bottled medical air (BOC, Manchester, UK) was used for the placebo exposure. All exposures were conducted double blind, in random order via a purpose built, closed circuit head only exposure system 10. Flow through the system for each exposure was maintained at 120 L·min–1 to prevent any significant rebreathing within the exposure circuit. The required concentration of SO2 was achieved by blending bottled medical air with bottled 60 ppm SO2 using mass flow controllers (Flow Tech Solutions, Stockport, UK). Verification of the delivered exposure gas concentration was made using an ultraviolet fluorescence gas analyser (API Corp, San Diego, CA, USA). For each exposure, the subject sat in a comfortable chair, with their head contained within the dome of the exposure system. The entry port in the wall of the dome was positioned within the breathing zone and the exit port was in the roof of the dome. A neck seal was achieved with a modified diving suit neck piece.

Measurements
Symptoms
Subjects were asked to record the degree of eye and throat irritation, cough, wheeze, sputum production and breathlessness before and at the end of each exposure, using a visual analogue scale (VAS) score.

Ventilation
A pneumotachograph (Vitalograph, Buckingham, UK) was incorporated in the exit limb of the exposure circuit, allowing the volume, duration and start time of each breath to be recorded. An oral thermocouple flow sensor (CASE, Biggin Hill, Kent, UK) was worn by the subjects which enabled us to determine the proportional partitioning of oral and nasal ventilation.

Lung function
Subjects performed spirometry before and immediately after their exposures, and at intervals for a further 4 h. Recorded parameters included forced expiratory volume in one second (FEV1), and forced vital capacity (FVC). Lung function measurements were made with a pneumotachograph (Fleisch) and the Vitalograph Spirotrac III system (Buckingham, UK), calibrated at the start of each study day. The best of ≥3 technically acceptable blows was taken as the measured value at each time point. European Community Coal and Steel (ECCS) predicted values were used.

Heart rate variability
Subjects wore a Holter recorder (Oxford Medilog 4500, Oxford Instruments, Abingdon, UK) for 30 min before, and for the duration of each exposure. The ECG data from the continuous Holter recordings were templated.

Outlyers and ectopics were identified and appropriately censored. R-R interval data were resampled at 3.41 Hz by applying a cubic polynomial and stationarity was approximated by least squares linear regression. Spectral analysis was performed using the fast Fourier transform and the application of a Hanning window of 512 points length. Powers were reported for each 5-min epoch of each exposure for each subject.

Data analysis
The HRV data were examined for stationarity. There was found to be considerable variability over the first four epochs and consequently comparisons have been restricted to data from the last seven epochs of each 1-h exposure.

Within group matched-pair analysis was used to compare the mean HRV spectral indices, the lung function parameters, the measures of heart rate and of ventilation between exposures. Paired t-tests were used for significance testing. Significance testing for between group comparisons was also by t-tests.


   Results
TOP
 Abstract
 Subjects and methods
 Results
Discussion
 References
 
Symptoms, ventilation and lung function
All exposures were well tolerated and were completed by all subjects. There were no differences in symptom scores in either the normal or the asthmatic group between exposures. In the normal group there were no significant differences in the ventilation parameters measured during the air and SO2 exposures. In the asthmatic group, SO2 exposure was associated with a small but significant increase in mean respiratory frequency relative to placebo (SO2 16.0 breaths·min–1, air 15.1 breaths·min–1, p=0.04, 95% confidence interval (CI) of difference 0.16–1.57 breaths·min–1), but the mean volume breathed did not differ significantly (SO2 318.8 L, air: 311.4 L; p=0.7). At least 95% of all breaths were nasal and there was no significant association between the frequency of oral breaths and SO2 exposure in either group. There were no significant changes in FEV1 or other lung function parameters with SO2 exposure in either group. Complete lung function data will be reported elsewhere.

Cardiovascular indices
There were no significant differences in maximum or minimum heart rates with SO2 exposure in either group (table 2Go). Examination of the spectral components with SO2 exposure showed a distinct pattern In normal subjects TP, HF and LF were all higher with SO2 exposure compared to air (table 2Go; p<0.05 for TP) while in the asthmatic group, all three indices were lower with SO2 exposure. LF:HF ratios were unchanged in both groups for each exposure.


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  		Table 2 Heart rate measures and frequency domain measures of heart rate variability by group

 
The difference in TP with SO2 exposure compared to air was +1730 ms2 in the normal group and –1021 ms2 in asthmatic group (p<0.003). For HF power the respective values were +964 ms2 and –539 ms2 (p=0.02) and for LF power, +437 ms2 and –572 ms2 (p=0.01).


   Discussion
TOP
 Abstract
 Subjects and methods
 Results
 Discussion
References
 
It has been demonstrated that exposure to 200 ppb SO2 is associated with reduced total, high, and low frequency power in asthmatic subjects and increased total, high and low frequency power in normal subjects. These differences in the autonomic responses of asthmatic and normal adult subjects to SO2 exposure occurred in the absence of detectable changes in symptoms or lung function. This implies that SO2 exposure at levels which can be frequently encountered during air pollution episodes in Europe 1, may have sub clinical effects. This indicates a systemic impact of a pollutant gas which may have implications in determining mechanistic pathways for both the respiratory and nonrespiratory effects of air pollutants.

The mechanisms of the health effects of SO2 are not completely understood. At higher concentrations than employed in this study, SO2 is a powerful bronchoconstrictor, i.e. at concentrations of around 400 ppb in asthmatics 5 and at concentrations >1,000 ppb in normal subjects 4. Such effects in normal subjects can be completely abolished with anticholinergic drugs, but are only partially reversed in subjects with asthma. These differences have been difficult to explain, but suggest that SO2 may produce bronchoconstriction in normal and asthmatic airways by differing pathways. It has been assumed that some of these effects may be mediated in the peripheral airways but this is unlikely to be the case for the present findings as at the concentration of SO2 employed (200 ppb) little if any of this highly soluble pollutant gas would be expected to penetrate beyond the trachea 11. This would imply that the upper airways, including the nose, pharynx or larynx may be important in determining these effects.

SO2 can activate rapidly adapting receptors (RARs) and C-fibres 12 in the upper airway and trachea, producing a centrally mediated increase in vagal tone resulting in distal bronchoconstriction. There is also some evidence that laryngeal C-fibre stimulation can result in local airway narrowing 6. Equally, SO2 may be able to induce local airway narrowing by the direct stimulation of sensory mucosal nerve endings through the process of neurogenic inflammation 13, although this remains to be proven for the human airway 3. Support for the latter explanation has come from work demonstrating that irritant nasal stimulation can increase total pulmonary resistance by inducing constriction while, at the same time, bronchodilatation occurs in the lower airways 14. This disparity between the laryngeal response and that of the lower conducting airways suggests that a single, vagally mediated mechanism is unlikely to be responsible and points to a local effect such as neurogenic inflammation.

The authors suggest that the present findings of autonomic changes are consistent with the existence of both these pathways (fig. 1Go). It is proposed that the primary autonomic impact that has been measured with exposure to SO2, is change in HF power. This is balanced by changes in LF power and consequently no overall change in lung function is seen. In normal subjects, the predominant pathway would appear to be through the RAR/C-fibre route, resulting in a central nervous system reflex with increase in vagal tone (increased HF power). In the subjects with asthma, it is proposed that local (proximal) airway narrowing (possibly through neurogenic inflammation) is the dominant response, observations of reduced HF power (i.e. reduced vagal tone) reflecting the CNS mediated, compensatory bronchodilatation of distal airways. The reduction in HF power is balanced by a reduction in LF power and thus no net change in measured lung function. This adds support to the hypothesis that neurogenic inflammation may be an important mechanism for airway narrowing in asthma in response to inhalation of SO2. The relative sensitivity of subjects with asthma to SO2 may reflect the increased exposure of their mucosal sensory nerve endings, due to the epithelial shedding, characteristic of asthma 15.



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  		Fig. 1.— Proposed autonomic pathways of sulphur dioxide mediated bronchoconstriction in normal and asthma subjects. —{blacktriangleright}: dominant pathway in asthmatic subjects; - - - {blacktriangleright}: dominant pathway in normal subjects; RARs: rapidly adapting receptors; CNS: central nervous system.

 
This hypothesis needs further exploration but, if shown to hold, would have implications beyond the understanding of the mechanisms of control of airway diameter in normal subjects and in subjects with asthma. Air pollution exposure has been shown to be associated with increased morbidity and mortality from both respiratory and cardiovascular diseases 16–20. While the respiratory effects of air pollution have been intuitive, understanding the mechanisms mediating cardiovascular effects has proven elusive. A number of potential mechanisms have been proposed, including the dynamic reduction of heart rate variability on pollutant exposure, with reduced HRV being associated with an increased risk of death following myocardial infarction 21 and in patients with heart failure 22. The present findings and those of others 23–26 suggest that pollutant exposure can provoke autonomic responses and that these responses may differ between subgroups of the population. It is possible that these autonomic responses may have trivial cardiovascular effects in healthy people, but may have more important consequences in those with underlying heart disease. Conversely it may be the inability of a diseased heart to respond to these autonomic modulations that mark individuals as being at increased risk of nonrespiratory morbidity or mortality during pollutant episodes.


   References
TOP
 Abstract
 Subjects and methods
 Results
 Discussion
 References
 

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