Occupational Asthma:Current perspectives |
Contents: |
Definition, and Frequency"Occupational asthma is a disease characterised by variable air flow limitation and/or airway hyper-responsiveness due to causes and conditions attributable to a particular occupational environment and not to stimuli encountered outside the workplace" (Bernstein et al 1993). Within this definition two types of occupational asthma can be distinguished:In the first instance, there is agreement, that the syndrome of chest tightness, wheezing, shortness of breath, dry cough etc, which appears after a latent period of occupational exposure constitutes occupational asthma. The second category of occupational asthma is that developing without a period of latency and often associated with exposure to high concentrations of irritants. Its symptoms may be somewhat different from that of asthma that follows a latent period. This is often referred to as Reactive Airways Dysfunction Syndrome (RADS).
Approximately 70,000 people in the UK according to the results of a sample questionnaire in the 1990 Labour Force Survey, believed that during a one year period they had symptoms of asthma caused, or made worse by substances breathed at work (Hodgson et al - Health and Safety Executive (HSE) Report - 1993). It is therefore an important cause of work-related ill-health, and is probably the commonest cause of new cases of occupational lung disease in general. Throughout the UK information about the newly diagnosed cases, and their causes is continuously collected through the SWORD scheme (Meredith and McDonald 1994). Workers may be unaware of the possible relationship between their symptoms and their work. Even if they do suspect a link, they may still be reluctant to present their concerns to any doctor, fearing adverse consequences for their employment.Since GPs see patients as individuals they may be at a disadvantage when compared to say, occupational physicians, in making the connection between work and symptoms.Employers often have inadequate surveillance procedures to measure the frequency of occupational asthma. Even when cases are brought to their attention, they do not always fulfil their legal obligation of reporting. Occupational physicians and chest physicians are usually well placed to diagnose cases. In the UK, di-isocyanate exposures, notably toluene di-isocyanate from exposures in occupations such as spray painting, and other work involving urethane varnishes or foams, certain waterproofing agents etc. clearly feature as the highest of the reported categories of causative agents (Meredith and MacDonald 1994). For more information about observational epidemiology of occupational asthma in the UK, please refer to SWORD (part of the THOR programme). Another important causal agent is colophony fume, from soldering especially in the electronics industry. Colophony arises from pine resin and contains abietic acid, and other resin acids which are used as fluxes in soldering. However, a very wide range of chemicals, and of agents of biological origin, have been described as causes of occupational asthma. Prevalence and incidence data for occupational rhinitis are limited but a Finnish study suggests that high molecular weight substances of biological origin - such as flour, wood dust, and animal dander - feature highest in the frequency of cases referred for investigation (Kanerva et al 1993). However, for the health care professional dealing with individual workers, or with groups of workers in a workplace, it is not the national incidence of the disease that matters. Rather, it is essential to get a grasp of the likely risk - i.e. the incidence in relation to defined jobs and tasks, and hence occupational exposures to specific agents. |
A Basis for Primary Prevention |
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| Can chemical structure be a useful tool in determining whether a substance may present an occupational asthma hazard? There are features of molecular structure of substances hazardous to health which appear more likely to be associated with a substance being a potential cause of occupational asthma (Agius et al 1991). An abstract of earlier work is available, and it is hoped to make more recent developments known in due course. | |
| Assessing exposure entails a scrutiny of who does
what,
where, and how. It requires a familiarity with the methods and
circumstances
of the work which, in combination with measurements, will produce a
clear
picture of the intensities and patterns of exposure. One of the
difficulties
in assessing exposures quantitatively is that the identity of the agent
directly responsible for, or most closely associated with, the risk of
asthma or rhinitis may be unclear, as is the case with baker's
asthma.
The photograph (right) was taken in a bakery, where flour dust was liberally scattered. The baker suffered from occupational asthma, and it was difficult for the employer to appreciate that something as apparently innocuous as flour could cause asthma, especially in conditions of high exposure. |
|
| There may be difficulties which
relate to the
time weighting of the monitoring: should eight-hour average exposure be
the focus or should it be peak exposures?
What about people who are infrequently exposed? When exposures carry the risk of occupational asthma and rhinitis, the assessment should proceed as follows:
Estimating the magnitude of health risk has to be tailored carefully to the actual circumstances under scrutiny. The conclusions should be based on two main factors:
To answer this question one needs to determine what knowledge exists of the harmful properties of the substance and how well founded that knowledge is. A thorough familiarity with the circumstances and patterns of exposure is required, and account must be taken of any special characteristics of the exposed population. For specific exposures, there is good evidence that the risk of sensitisation is related to the exposure level. In other words - the higher the concentration of inhaled agent, the greater the likelihood of becoming sensitised and of experiencing symptoms of rhinitis and/or asthma. However it is difficult to set exposure limits below which exposures can be regarded as 'safe' in an absolute sense - although the risk might be very low. Moreover it is possible that once sensitised, the airborne concentrations at which symptoms could be provoked might be even lower than the concentrations responsible for sensitisation in the first place. Airborne exposure to respiratory sensitisers may carry a risk of asthma. Since this may be a potentially life-threatening condition, one must be confident that the risk of contracting it is very low before concluding that all reasonably practicable measures have been applied in implementing control through containment and ventilation. |
|
| The most effective means of control is to prevent
exposure
altogether, either by not doing the task in question or by substituting
the sensitiser for a less harmful material, although this is not always
feasible. For example if a di-isocyanate based paint or varnish is
being
used, one should question whether a much less hazardous paint which
simply
dries out without curing can be applied instead. This might entail the
need for re-painting at more frequent intervals, depending on the
circumstances.
The photograph (right), depicting control measures, shows a pharmaceutical process worker tipping dust from a tray into a hopper.It illustrates a combination of control measures used when handling a substance, in the pharmaceutical industry, that may cause occupational asthma. The hopper is provided with local exhaust ventilation; the tray is covered by polythene, and the operator is wearing personal protection including an airhood, which includes a personal supply of breathing air. |
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| Similar principles of protection may be applied in a wide variety of industrial circumstances, involving exposure to man-made chemicals, or to natural products. Man-made exposures range from car spray painting with di-isocyanates, to soldering with colophony flux or the manufacture or use of acid anhydrides to make resins. Naturally occurring biological agents which may cause sensitisation range from mammalian urinary proteins, to locusts used in laboratories, to the processing of foods such as salmon, crabs, prawns or shrimps, and to rubber latex. | |
| The second photograph (right), illustrating
control measures,
shows a radiographer in a general hospital. The processing of X-ray
films
may be associated with the release of various respiratory irritants,
such
as sulphur dioxide, glutaraldehyde, and acetic acid. Some of these may
cause asthma.
By using sealed bottles of photographic reagents and introducing them into the processor using a closed system, as shown in the image, exposure can be considerably reduced. Inadequately controlled glutaraldehyde exposure in the health service, notably in the cleaning of endoscopes, such as in bronchoscopy and gastroscopy, has been responsible for serious ill-health in some nurses, and other health care workers. Formaldehyde is another aldehyde implicated in the causation of occupational asthma. |
|
This is the chemical formula of glutaraldehyde:
O:CH.CH2.CH2.CH2.CH:O |
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| Other methods of control might need
to be considered.
For example,it might be possible to change the formulation of enzymes
from
fine dust into granules - which are less likely to generate aerosols -
or to increase the relative humidity of environments where
cyanoacrylates
are handled (since water vapour will cause cyanoacrylate monomer to
polymerise
and become practically harmless by comparison).
Personal protection, albeit the last line of defence, may play an important role in situations where control at source is clearly impracticable. Thus, for example, in paint-spraying with di-isocyanates, full-face respiratory protection is the bare minimum level of acceptable protection. In animal handling laboratories, powered filtering facepiece respirators may be a useful adjunct to other forms of control. Similarly, personal protective equipment would clearly be appropriate if a process plant was undergoing maintenance or being upgraded. |
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ConclusionThe number of recognised occupational respiratory sensitisers is likely to increase. Many are probably already in existence but have not yet been recognised. Others have yet to be discovered or manufactured. Many novel chemical entities, designed for a wide range of purposes - such as high-performance adhesives and resin monomers - have chemical properties which render them especially capable of sensitisation.Our capability to predict hazards should improve, and better control methods should become available. In those instances where prevention or early detection fail, affected workers must hope that the paths to rehabilitation and to compensation will become smoother. |
Case Studies |
ReferencesEvidence based guidelines for the prevention, identification, and management of occupational asthmaBernstein IL, Chan-Yeung M, Malo J-L, Bernstein DI (1993).Asthma in the Workplace. Marcel Dekker, New York, pp1-4.Health and Safety Commission (1995) Control of Substances Hazardous to Health Regulations 1995: Approved Codes of Practice: General COSHH ACP (Control of substances hazardous to health); Carcinogens ACP (Control of carcinogenic substances); and Biological agents ACP (Control of biological agents). One-volume set of three ACPs (ref L5) ISBN 0 7176 0851 4. Available from HSE Books and from approved outlets, price 6.75. Health and Safety Executive (1990). (HS(G)61) Surveillance of people exposed to health risks at work. HSE Books. ISBN 0 11 885574 3. Health and Safety Executive (1991) (MS25) Medical aspects of occupational asthma. HSE Books. ISBN 0 11 885584 0. Health and Safety Executive (1994) Preventing asthma at work. How to control respiratory sensitisers. HSE Books. ISBN 0 7176 0661 9. Hodgson J T, Jones J R, Elliott R C and Osman J (1993) Self- reported work-related illness. Health and Safety Executive Research Paper 33. HSE Books, Sudbury. Kanerva L, Vaheri E (1993) Occupational allergic rhinitis in Finland. Int.Arch.Occup.Environ.Health,64,565-568. Meredith SK and McDonald JC (1994) Work-related respiratory disease in the United Kingdom, 1989-1992: report on the SWORD project. Occup Med, 44, 183-189. Newill C A, Evans R and Khoury M J (1986) Pre-employment screening for allergy to laboratory animals: epidemiologic evaluation of its potential usefulness. J.Occup.Med.28,1158- 1164. Seaton A, Agius R, McCloy E and D'Auria D (1994) Practical Occupational Medicine , Arnold publishers.London.pp.78-79,99, 133-134. Venables K, Dally M, Nunn A, Stevens J, Stephens R, Farrer N, Hunter J, Stewart M, Hughes E and Taylor A N (1989) Smoking and occupational allergy in workers in a platinum refinery. BMJ,299,939-942. |
Copyright, acknowledgement, and disclaimer.This account is reproduced here by permission of the editor of Occupational Health Review, (OHR) and is an abbreviation, and subsequent adaptation of a much longer version published as a series of four articles on 'Occupational asthma and rhinitis' published in OHR in 1995:
While this account has been written and published in good faith, no legal responsibility is accepted for its contents or their interpretation. Workers who suspect that they might have occupational asthma or rhinitis should consult their general practitioner (and occupational physician if their workplace employs one). |
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Asthma LinksPages relevant to Occupational Asthma:Evidence based guidelines for the prevention, identification, and management of occupational asthmaOccupational asthma - Review."Asthma at Work - your charter" (from asthma UK)Airborne environmental pollutants and asthma Research by the author and colleagues on occupational asthma hazard prediction based on quantitative structure activity relationships: Experimental hazard prediction. The OASYS (www.occupationalasthma.com) website Occupational Asthma - INDEX - written by one of our postgraduate students The Occupational Asthma Server- search by agent or by occupation More asthma links are available in a section of the directory |
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