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C 371 4
THE HEALTH HAZARD AT WITTENOOM
"No government, when it knows of a health hazard, can h*p it's employees working m that situation".
Mr Ray Young Minister for Health 1.12.78
The medical evidence supporting the Minister's statement quoted above is contained in scientific literature and the results of investigations conducted by the Public Health Department.
In 1959 when it was first observed that mesothelioma was affecting certain
people who had lived in the asbestos areas in the Northern part.of the Cape
Province of South Africa (1), (2), the occupational health physician in the
Western Australian Department of Public Health was investigating the occurrence
of silicosis and asbestosis in miners employed by Australian Blue Asbestos
at Wittenoom. X
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In a memorandum from the Occupational Health Physician to Mr O.A. Allen, Australian Blue Asbestos Pty Ltd, dated 5th October 1961 it was stated:
"This Department is becoming increasingly concerned at the nujctoer of employees and ex-employees of Wittenoom who are ^^aueucug^as patients suffering from asbestosis or. silicosis -
Dr McNulty informs me that he considers a number of dust counts at Wittenoom to be too high."
A meeting between representatives of the Health Department, the Mines Department and Australian Blue Asbestos was held in Perth on 10th October, 1961 and it was agreed that attempts would be made to improve the ventilation in the mine, and the mill and to institute a system of dust counting. However, it was recognised that existing methods of dust counting had definite limitations.
The first case of mesothelioma occurring outside South Africa was detected
in a Wittenoom ex-miner by Dr J McNulty and reported in the Medical Journal of Australia in 19^2 (3).
In the following year another report from South Africa postulated an unusual risk from exposure to blue asbestos and a rising incidence of mesothelioma from exposure to it during ensuing decades (4).
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In 1965 Dr McNulty reported 7w 'K)4-
"The asoestos miners m this State have been exposed to such heavy dust concentrations at work it has always seemed a rasonahle precaution to advise against the use of tailings for surfacing on the grounds that the workers should not be exposed to dust during their leisure hours as well. Wagner has shown that out of 120 known cases of malignant pleural mesothelioma in the Cape asbestos fields, more than half had never worked in the industry but had merely lived in the vicinity of a mine or mill; included were females where only contact was with the overalls of miners, a radiographer who visited the mines only to take periodical chest x-rays, and an accountant who audited the books at an asbestos mine.
Nevhouse has shown similar situations in Barking around the London Cape Asbestos factory and McCaughey in Belfast. Grazing animals around the sines in South Africa have developed asbestosis. Kiviluto in Finland has found pleural calcified plaques of a type peculiar to asbestos workers to be common in farmers and house-wives living near anthophyllite mines. .Sluis-Creaer has reported similarly from South Africa."
Dr McNulty visited Wittenooa and made personal contact with the mine management and various townspeople to warn against the use of mine tailings in the town. This visit was recalled recently in a letter to the West*Australian, written by a former headmaster of the primary school at Wittenoom.
**A senior officer of the Public Health Department was passing the the school and he saw the tailings. He came into the school in an obvious stats of anxiety to warn me against spreading them. He said they were known. to., be a serious health hazard and quoted South African experience and medical research."
In October 1965 a letter from the f-Connissioner of Public Health to the Shire Clerk, tableland Shire Council contained the following statement:
"Over past years, our attitude has been made perfectly clear to the Mines Department and to the Management of the Mine on the use of tailings, by the Minister for Health, myself and my officers. Hie Management of the Mine has been given the opportunity to examine all the literature we have available on the subject. As your Council has always contained
members associated with the Management of the mine, I cannot accept < 1i c a suggestion that the Council as a whole is ignorant of the Health
Department's attitude in this matter-------------
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My personal opinion on the asbestos tailing situation and the hazard to health associated therewith is that, as it exists in Wittenoom today, it forms a complete prohibition to the future development of Wittenoom as a residential area until all tailings are adequately covered with several inches of soil, or preferably removed or sealed in bitumen. X appreciate that this is a costly business and before taking more concrete action in this respect I have asked Dr McNulty to place the situation before several world authorities on this matter, to obtain the benefit of their opinions. When we receive these opinions X will communicate them to you; in the meantime asbestos tailings must be left where they belong - in the mine."
At that time, in 1965, there was no recognised health standard for asbestos dust. Dr McNulty sought the advice of experts overseas concerning the use of asbestos mine tailings for road surfacing. In reply the following opinions were received:
"I believe that the use of asbestos tailings on the surface of roads and on the surface of playgrounds, amounts to a deliberate sealing of the ground with a cancer producing substance, and therefore is contrary to every principle of prosecution of disease in man and contrary to all purposes of public health. One should avoid the mistake of not recognising the inevitability of serious disease, just because an immediate effect is not apparent."
Thomas ? Mancuso, M.O. Research-.Professor University of*Pittsburgh January 19th, 1966
"In view of the South African experience and mounting epidemiologic evidence from other sources, it seems to me that you are fully justified in doing whatever is necessary to prevent the use of blue asbestos in West Australia."
w. Clark Cooper M.O. Research Professor and
Lecturer Occupational Health University of California November 19, 1965
"Whether exposure, which might be associated with environmental
contact consequent upon using asbestos paved roads or playgrounds
would be injurious I do not, of course know. Wagner's observations
are suggestive, but not conclusive. Nevertheless, it would appear
to me to be hazardous to assume that such contact carries no risk.
I believe it is considerations such as this which recently lead to
the hannina of nshosros .is /\ nlavroom imrrrvil in CM i
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schools and a similar recommendation by the U.S. Commissioner of Education."
Irving J. Selikoff M.D. He ad Section on Environmental
Health The Mount Sinai Hospital November 1, 1965
"Certainly the use of such tailings results in some measure of aerial pollution with fibre and this is a potential danger."
G.K. Sluis-Cremer Director Miners Medical Bureau Johannesburg 29 October, 1965
"I think the simple answer to your letter is, stop it at once! Z think there are now ample grounds from South African experience and from your own in taking all possible care to avoid inhaling crocidolite dust, and thae the use of it for surfacing roads and playgrounds is really quite unacceptable in the light of present evidence (which) -
fully confirms that there is a striking difference between the mesothelioma risk in the crocidolite area as coscared with the amoeite and chrysotile areas. No tumours have yet been observed from either of these two latter regions. The total number of tumours in South Africa has now risen to something like 170."
J.C. Gilson F.R.C.P. Director Pneumoconiosis Research.
Unit PENARTH 27 October, 196S
"As things stand it seems to me that the authorities cannot contemplate the contained existence of this potential hazard, and that the use of this potential hazard, and that the use of tailings for road surfacing must be prohibited, and that existing roads and playgrounds surfaced with tailings should be sealed."
W.T.E. McCaughey Professor of Pathology School of Pathology Trinity College DUBLIN 25 October, 1965
In 1966, for the first time reasonably reliable dust counts in the mine and mill were obtained. An expert industrial hygienist reported:
"Typically a hand bagger was e^osed to a respirable dust concentration of 3000 narri.cli*s per rr of which 100 wore fibre*'"! lona^r fh
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industry is said to work to an informal maximum of 4 fibres per cc but this material is white asbestos - whereas the material investigated was blue asbestos - crocidolite - which is quite different." (5)
Shortly after this investigation was completed, in December 1966, the mine ceased operations.
In October 1966, Dr McNulty received a letter from the Shire Clerk, Tableland Shire Council stating that an undertaking had been given by Australian Blue Asbestos not to sell or supply tailings except for use in bitumen or cement work and that the Council had ceased using it.
In January 1967 Dr McNulty wrote to the Education Department stating: "The general public, especially children must not be exposed to .t f the risk of inhaling blue asbestos fibre, and quoting the fact that the lose of blue asbestos mine tailings for road surfacing and
I dumping close to schools have been shown to be a serious health hazard in the Cape Province of South Africa. He also said no loose fibre which could become air borne should be permitted in populated areas."
In January 1967, it was suggested that the asbestos mine at Wittenoom
may be re-opened. This action was opposed by Or D.O. Latham, Physician in Charge, Occupational Health, Or J. McNulty, Physician Occupational Health and Dr P.F. Maguire, Mines Medical Officer. uuTconx&ents on the health hazard were reported in the Nest Australian of December 8, 1966.
In may 1968 the Health Inspector, Mr Kennedy wrote to say that the town people were adamant that fresh supplies of tailings were not being used. His observations indicated the need to question this statement.
A subsequent letter was received from Mr Graham, Area Manager, Hancock and Wright stating he was not aware there were any restrictions on the use of tailings. On receipt of information to that effect from the Health Inspector, he had a notice erected stating "Removal of Tailings under any circumstances strictly prohibited."
In correspondence between Or McNulty and the Shire Clerk it was agreed that mine tailings could be incorporated in concrete if they were transported safely and if unused tailings were returned to the dump or spread or buried in such a manner that loose fibre would not blow about.
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In 1968, the British Occupational Hygiene Society set up a conmittee to examine the available evidence and to reach an .agreed solution for exposure limits to asbestos (6). They calculated that exposure to 2 fibres per cm3 for 50 years or 4 fibres per cm3 for 25 years or 10 fibres per cm^ for 10 years would give a 1% risk of asbestosis.
In 1969, Regulations incorporating these standards and governing all work liable to create asbestos dust were introduced in Great Britain. The standard for 'blue' asbestos, generally considered the most hazardous in relation to nmsothelioma, was ten tines more stringent (0.2 fibres per cc). Since 1970 British manufacturers have voluntarily agreed not to import blue fibre.
During the next five years the B.O.H.S. standard for chrysotile asbestos was criticised on a number of grounds. It had been established on very little dat^it was based on the possibility of occurrence of asbestos;! which is of joiner importance relative to cancer and it used fibre concentration x years as a measure of exposure. The Public Health Department became increasingly concerned about a possible public health risk in Wittenoom.
`b'/lM'rC Mr W Moyle completed an inspection of Wittenoom on 25, 26th and 27th October 1973. His report contains the following observations: "Streets are sealed but in all except one or two cases have been made with mine tailings. Evidence of unsealed tailings may be noted on the sides of the roads. In the early days it is obvious tdaat people used tailings to make drive-ins for their houses and some even used them to cover garden areas. Large areas covered by tailings include the front of the Wittenoom Club, the car park for the Club, the Convent playground, the vehicle parking site near the State School and the tennis courts. The race course is completely covered with tailings and it is interesting how the fibres have become pulverised and separated with rain to form concentrations in the hollows made by hoof marks. At the airport tailings have been used, but a sealing programme is intended for the middle of November this year. The Shire Councillor, Mr McGuire, said that the Shire has not used tailings for years because they are aware of the health danger and also because it is now too expensive.
I contacted Mr Solitho, Manager for Hancock and Wright, at Wittenoom* His office is in the Gorge where approximately 16 families are housed. Mr Bolitho said these families are employed by Hancock and Wright and are engaged in exploration and maintenance work. He said screenings are now sold at $15 per ton to discourage anyone from using it. He is prepared to sell it to anyone making concrete. He said tourists
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Sables of airborne dust collected from Wittenoom at that time were /]
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and not examined until 1975. The results were reported as A
follows:
State School Police Station Airport Woodward 5th Ave S3 4th Ave Back of Hotel
Personal samples (fibres/cc) 0.16 0.05 0.05 0.88 0.05 0.11
Fixt-flo sauries (fibres/cc). 0.03 0.005 0.03 0.006 0.004 0.006
Zt was stated that; "No explanation can be offered for the large difference in fibre counts between the personal and Fixt-Flo samples, in both groups of samples the number of fibres appeared to be related closely to the total dust concentration as indicated by discolouration of the paper and represented only a very small proportion of the deposit."
The method of sampling was considered to be unsatisfactory, and it was decided to repeat the investigation when a more accurate method became available.
Zn July 1976 a Draft Code of Practice for "The Estimation of Airborne Asbestos in the Working Environment became available and discussions were started with the industrial hygienist in the School of Public Health and Tropical Medicine in Sydney concerning the use of an approved sampling method for asbestos dust for Wittenoom.
Zn July 1977, Dr Cumpston and Mr D Sykes visited Wittenoom.
1. Ten saaples of airborne dust were taken while driving around the town at 40 km/hr with the saapling head protruding from the boot of the car.
The fibre counts (fibres/cc) were: 1.3 3.6 0.8 1.2 0.8 1.3 3.0 1.7 1.9 2.1
0 Average 1.77 fibres/cc.
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2. Fixt-flo samples from a.?. Garage. 1. No asbestos fibres identified in the sample. 2. Two particles of crocidolite were identified in the sas^le, one of which conformed to the NHMRC criteria for fibre identification, the other being a nonrespirable fibre bundle.
3. Dust in old houses opposite Shire workshop. No asbestos identified in the sample.
4. Sand from creek bed approximately 5 km from Wittenootn. The sample contains approximately 0.2S percent of crocidolite in millimetre sized particles which shed fibres of respirable dimensions if agitated.
5. Dust from outside vacuum cleaner bag. Dumar Motel. Respirable fibres are produced in the sample, their concentration, relative to the total mass of the sasple, being in the same order as in these samples which were collected by the personal sandier. Most of the fibres are between S mm and SO tin in length and less than 1 on in diameter. The coarser fibres include a high proportion of crocidolite.
6. Asbestos tailings collected from the mine site. The sample contains approximately S percent of crocidolite, mostly in discrete matted aggregates of crushed fibre. This material is susceptible to shedding particles of respirable size.
7. Three samples of dust from a C.E.R.L. dust gauge mounted in the
school grounds.
Crocidolite .. Respirable Fibres
1 present . not detected
2
present
present
3
present
present
In each case the crocidolite is estimated to be less than 1% of the sample. More than seventy-five percent of the crocidolite is greater than respirable size.
8. Seven, sauries of vacuum cleaner dust from various residances around
the town of Wittenoom.
Crocidolite Respirable Fibres
...coan.
Primary School 68 6th Ave Cnr Beasley St and
7th Ave 66 5th Ave
Crocidolite
present present present present
Pespirahle Fibres
present present
present
not detected
In all the samples crocidolite is estimated to be less than one
percent of the sample. The material from the Primary School has
the greatest amount. At least 75 percent of the fibre is of
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respirable size. In the case of the Primary School this figure
exceeds 90 percent, the school has the coarsest crocidolite fragments.
In 1977 x-rays were taken of 146 adult members of the population in Wittenoom and no definite evidence of asbestos related disease was detected in any x-ray.
At that time Or Cumpston reported: "There is no doubt that the population in this town would be exposed to the inhalation of asbestos fibres. The problem to be resolved is whether such exposure could produce asbestos related disease. If we take the allowable community exposure to be 1/10 of the British Occupational figure for blue asbestos (0.2 fibres per ca^) it is unlikely that the resultant figure of 0.02 fibres per cm^ would represent the continuing exposure of any individual in the connunity. However, one cannot altogether discount the possibility chat mesothelioma may arise in an individual exposed to asbestos in wittenoom. Therefore it is recomended that: a. no future development or growth of the town should be
permitted; b. investigations described in this report should be repeated
each year. I*
In November, 1977, a sample of dust from a personal sampler worn by a Mines Inspector for half an hour outside the school and one hour outside the hotel was found to contain approximately 0.2 fibres per cc of filtered air.
This figure equals the threshold limit set for crocidolite by the British Occupational Hygiene Society for occupational exposure, it was decided that the Division should embark on a more extended sailing program."
Soon after this report was written information from overseas, an
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Exposure to Asbestos, a report of a working-group prepared for the Commission of European Communities, and the I.A.R.C. monograph no. 14 on asbestos. The first concludes from information on environmental contamination that no convincing evidence exists in Western Europe of increased risk through true ambient exposure to asbestos - in air, water, drugs, beverages or food - though the possibility of such a risk cannot be categorically denied. Paraoccupational exposures of family and neighbourhood and leisure-time working with asbestos-containing products are singled out as an area of concern. The X.A.R.C. report, looking at experimental as well as epidemiological evidence, concludes more pessimistically that "it is not possible to assess whether there is a level of exposure in humans below which an increased risk of cancer would not occur."
The editorial ended by saying: "An advisory committee of the Health and Safety Conaaission is examining not only health aspects of asbestos but also economic factors in the control of hazards and substitution by alternative materials such as man-made mineral fibres. A report is expected in 1978, and revised codes of practice and standards will doubtless follow." (7)
Later in 1978, it was reported in the Royal Society of Health Journal, February 1978, that:
"The Asbestos Information Comittee accept that the asbestos concentration presenting a negligible hazard for a life-time's non occupational exposure if 0.04 fibres/ca^ , whereas Kelly has suggested that the v concentration should not exceed the normal background level." (9)
In May 1978, an article^in the Lancet reported the death of 65 females
from mesothelioma,
of these had routinely laundered their husbands
or fathers clothing, but had no industrial contact with asbestos. (8)
In July 1978, Dr Cumpston visited Wittenoom and explained to residents
chat there is a slight health risk to adults following prolonged residence
in the town, but the hazard is greater for children. He arranged for a
volunteer group of citizen's to wear personal dust samplers. A trial
period of sailing was found to be technically satisfactory and the
following results were obtained:
Fibres per cm3
1 0.08
2 0.09
3 0.01 .1 n.*l
u cone.
Fibres per ca^
9 0.01 10 0.06 11 0.12 12 0.02
Average 0.075.
It was therefore decided that the presumed health risk to residents at Wittenoom, particularly to children was confirmed to a sufficient degree to convey this medical information to the Minister for Health.
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