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How are the physical and chemical properties of chrysotile asbestos altered by a 10-year residence in water and up to 5 days in simulated stomach acid?

Although there have been a number of studies on the ingestion of asbestos, few studies exist on how the chrysotile asbestos itself is altered by the exposure to the acid stomach environment. This study has found that there are changes in the physical, chemical and surface properties of chrysotile asbestos as a result of exposure to water, strong acids, and simulated gastric juices. It was observed that the charge on the surface (the zeta potential) is changed from positive to negative; the surface becomes silicalike; and the magnesium is lost from the fibers of asbestos upon exposure to water and acid. It was also noted that the smaller the fiber diameter, the faster the loss of the magnesium. Notable among the changes in physical properties is a change in the refractive index. This means that asbestos exposed to acids or water may not be detectable using the dispersion staining techniques that identify asbestos based on the refractive index. Other physical property changes include the destruction of the gross crystallinity of the fibers. The x-ray diffraction signal disappears when fibers are exposed to acid. However, this study shows that the fibers may still be detected by electron diffraction. It appears that upon acid exposure, the magnesium ions are leached out, leaving a magnesium-free silica network. A positive ion, possibly the proton (H+) or the hydronium ion (H3O+), replaces the lost magnesium ion.

Asbestos↗

Present status of asbestos mining and related health problems in India--a survey.

At present in India more than thirty mines are in operation. It produces 2800 tones of asbestos per month (mainly chrysotile and tremolite) and in recent years substantial quantity (-70%) is imported from Canada. The quality of asbestos produced in India is very poor. The mining and milling and other related processes expose the people to cancer and related diseases. Women are more affected by their exposure in processing unit compared to male who are generally working in mines. Direct and indirect employment in asbestos related industry and mine is around 100,000 workers. Latency period (length of the time between exposure and the onset of diseases) in India is estimated to be 20-37 yr. The causes for lung and breathing problem are mainly due to obsolete technology and direct contact with the asbestos products without proper precaution, because in India asbestos are sold without statutory warning. This paper reviews health effects (such as fibrosis, sequelae, bronchogenic cancer, and malignant mesothelioma) on the Indian mine workers caused due to asbestos mining related activities with respect to their present day condition.

Asbestos, Amphibole↗

Asbestos exposure and mesothelioma in South Africa.

OBJECTIVES: To describe the exposure experiences of South African mesothelioma cases, with emphasis on the contribution made to the caseload by different fibre types, the proportion of subjects with no recall of asbestos exposure and only environmental contact, and the importance of putative causes other than asbestos. DESIGN: A multi-centred case-control study. SUBJECTS AND SETTING: 123 patients with mesothelioma interviewed by trained interviewers in study centres established in Johannesburg, Kimberley, Pretoria, Bloemfontein, Cape Town and Port Elizabeth. RESULTS: A convincing history of asbestos exposure was obtained in the overwhelming majority of cases (only 5 cases had unlikely asbestos exposure). Twenty-three subjects had worked on Cape crocidolite mines, 3 at Penge (an amosite mine), 3 on mines producing amosite and Transvaal crocidolite and 1 on a Transvaal crocidolite mine. Exclusively environmental exposure accounted for at least 18% of cases; 91% of these cases (20/22 subjects) had had contact with Cape crocidolite. There was a relative paucity of cases linked to amosite and no convincing chrysotile case. Non-asbestos causes occur rarely, if at all, in South Africa. CONCLUSION: The preponderance of crocidolite cases, followed by amosite and then chrysotile cases, is consistent with the view that there is a fibre gradient of mesotheliomagenic potential for South African asbestos (crocidolite > amosite > chrysotile).

Asbestos, Amosite↗

[Railway use of asbestos-containing rubble: environmental hygienic aspects].

The paper presents the results of a study of the gravimetric and counting concentrations of respirable asbestos fibers while working with sand-and-crushed stone mixtures, obtained from the concentration of chrysotile asbestos, at distances of 25, 50, and 100 m from the working place, as well as in a car saloon when the electric train passes along the area of these operations following an hour, a day, and a year after the completion of work, in warm and colds seasons of a year. It is concluded that the use of asbestos-containing sand-and-crushed stone mixtures on the railway leads to a higher anthropogenic asbestos load on the population living in the railway right-of-way, on railway workers and passengers. In this connection, it is necessary to evaluate risk factors of asbestos-induced diseases among the above contingents. The authors consider that due to the fact that asbestos-containing sand-and-crushed stone mixtures are well wetted with water, followed by the formation of a firm surface crust that prevents dust formation, as well as the short duration and rare frequency of operations relating their change, it is necessary to irrigate the repair areas with water or surfactant liquids after work termination.

Asbestos↗

[Hygienic aspects of the production of asbestos substitutes].

Due to the high level aggressiveness of asbestos, more attempts have been made in the recent years to replace asbestos by other artificial mineral fibres. In this connection, the labour conditions were studied in the basalt and carbon fibres processing sites. The major occupational hazards of these sites included basalt and carbon fibres dusts, heating microclimate in some working zones and physical overload. An intratracheal experiment revealed a lower degree of fibrinogenicity of the basalt and carbon fibres as compared to chrysotile asbestos. The number of the induced mesothelioma in the intraperitoneal introduction of basalt and carbon fibres was markedly lower than in case with chrysotile asbestos. Hygienically, asbestos should be replaced wherever possible, and the dust control measures should by no means be inferior to those with asbestos.

Asbestos↗

[Environmental interstitial pneumonia caused by asbestos. Study of a Turkish family exposed to tremolite].

Environmental exposure to asbestos, as observed in Anatolia (Turkey), usually results in pleural pathology (plaques and mesothelioma). We report the case of a 50-year old woman who, until the age of 50, had lived in Eregli, central Anatolia, a region where inhalation of environmental asbestos is responsible for a high prevalence of pleural diseases. Radiology showed diffuse interstitial pneumonia without pleural involvement. Bronchoalveolar lavage brought back asbestos bodies (AB) in concentrations of 4,250 per millilitre. All were made of tremolite, a non-commercial variety of asbestos. The patient's family was investigated by chest radiography and search for AB in sputum. The husband, who came from the same town as his wife and had been exposed until the age of 45, had the classical response with bilateral pleural thickening but no parenchymal abnormalities; 2 AB were found in his sputum. The 3 sons, exposed for 10, 13 and 20 years respectively, had normal radiograms and no AB in their sputum, except for the older (3 AB) who had been exposed for 20 years. These cases illustrate the importance of environmental exposure to asbestos which may produce lesions similar to those observed in industrial exposure. Only mineralogical examinations can determine whether the asbestos is environmental or industrial.

Asbestos↗

Usefulness of combined light and electron microscopy: evaluation of sputum samples for asbestos to determine past occupational exposure.

Ferruginous bodies (FB) in sputa are recognized as an indicator of past exposure to asbestos. However, a great variability exists in FB production, even in individuals with a history of occupational exposure. A further complication in interpreting the presence of FBs in sputa is that all individuals in modern society are exposed to asbestos and, in lung tissue studies, have been shown to harbor appreciable numbers of asbestos fibers. Thus, some of these individuals should occasionally produce FBs in their sputa. The present study was undertaken to determine if uncoated asbestos fiber content could be used to better discriminate occupationally exposed individuals from the general population. Randomly selected sputum samples from 12 former workers in an amosite asbestos plant and 12 controls were studied. The samples were prepared for the study by digesting the sputa in sodium hypochlorite. The digests were filtered through 0.2-microns polycarbonate filters for collection of particulates. The filters were screened for FBs by light microscopy at 200 X, and the presence or absence of uncoated asbestos fibers was determined at 5000 X in an AMRAY 1000A scanning electron microscope. The use of electron microscopy revealed the presence of commercial amphiboles in the sputa of the occupationally exposed individuals and enabled a differentiation of these samples from those of the general population.

Adult↗

Characterization of asbestos bodies and uncoated fibers in lungs of hamsters.

Dimensional changes of asbestos bodies and uncoated fibers and the leaching of magnesium from the surface of chrysotile after a single intratracheal injection (1 mg) were investigated in male hamsters. The animals were sacrificed at 1 day, 6 months, 1 and 2 years later. In addition to histopathological observation, asbestos tissue burdens were investigated in 25 microns thick sections of the lungs. The sections were ashed in a low-temperature asher to be extracted with carbon film. The carbon extracted ashed sections were investigated by high resolution analytical electron microscopy to characterize asbestos fibers and asbestos bodies. Pulmonary interstitial and pleural fibrosis were observed after 6 months and later on. Light microscopically, asbestos bodies were observed after 6 months; their incidence subsequently increased with the lapse of time after the injection. Asbestos bodies measured on light micrographs became longer with the lapse of time. This suggested that the coating of chrysotile fibers had been continuously progressing in the lung. Geometric means of length and width of uncoated chrysotile fibers seen by transmission electron microscopy in animals at 1 year (length: 1.4 microns; width: 0.057 micron) or 2 years (1.2 microns, 0.047 micron) were greater compared with those of animals at 1 day (0.9 micron, 0.041 micron) or 6 months (0.9 micron, 0.037 micron) after instillation. These findings suggested that short and thin chrysotile fibers were cleared from the lung.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

[Dynamic studies of the leukocyte phagocytic activity after exposure of rats to asbestos and basalt fibers].

The paper presents the results of the dynamic one-year follow-up of the phagocytic activity of Wistar-rats peripheral blood leukocytes following intraperitoneal administration of asbestos and basalt fibres (Man-Made Mineral Fibres--MMMF). We investigated the phagocytic activity of leukocytes in peripheral blood following intraperitoneal administration of asbestos and basalt fibres to rats 2, 24, 48 h as well as 1, 2, 4, 8 weeks and 6 and 12 months after dosing. We investigated the time dependent of the changes of relative granulocytes count, percentage of phagocytizing cells from leukocytes, percentage of phagocytizing granulocytes and percentage of phagocytizing monocytes. The results of our experiment showed that asbestos and basalt fibres differed in their effects on the parameters studied. Granulocyte count as well as the phagocytic activity of leukocytes during the one-year dynamic follow-up in both dust--exposed groups of animals were found to change in two phases, characterised by the initial stimulation of the acute phase (I), followed by the suppression of the parameters in the chronic phase (II). Exposure to asbestos and basalt fibres led, in phase II, to impairment of the phagocytic activity of granulocytes. Asbestos fibres at the same time significantly decreased also the phagocytic activity of monocytes. Exposure to basalt fibres did not affect the phagocytic activity of monocytes in phase II. It follows from the results of the experiment, that the monocytic component of leukocytes probably plays an important role in the development of diseases caused by exposure to fibrous dusts and basalt fibres have smaller biological effects compared with asbestos fibres.

Animals↗

Asbestos causes stimulation of the extracellular signal-regulated kinase 1 mitogen-activated protein kinase cascade after phosphorylation of the epidermal growth factor receptor.

Asbestos fibers are human carcinogens with undefined mechanisms of action. In studies here, we examined signal transduction events induced by asbestos in target cells of mesothelioma and potential cell surface origins for these cascades. Asbestos fibers, but not their nonfibrous analogues, induced protracted phosphorylation of the mitogen-activated protein (MAP) kinases and extracellular signal-regulated kinases (ERK) 1 and 2, and increased kinase activity of ERK2. ERK1 and ERK2 phosphorylation and activity were initiated by addition of exogenous epidermal growth factor (EGF) and transforming growth factor-alpha, but not by isoforms of platelet-derived growth factor or insulin-like growth factor-1 in mesothelial cells. MAP kinase activation by asbestos was attenuated by suramin, which inhibits growth factor receptor interactions, or tyrphostin AG 1478, a specific inhibitor of EGF receptor tyrosine kinase activity (IC50 = 3 nM). Moreover, asbestos caused autophosphorylation of the EGF receptor, an event triggering the ERK cascade. These studies are the first to establish that a MAP kinase signal transduction pathway is initiated after phosphorylation of a peptide growth factor receptor following exposure to asbestos fibers.

Animals↗

Pulmonary mineral fibers after occupational and environmental exposure to asbestos in the Russian chrysotile industry.

BACKGROUND: As an indicator of occupational, domestic, and environmental exposure, the level and type of asbestos fibers were determined from lung tissue samples of workers and residents who resided in the area of the world's largest asbestos mine at Asbest, Russia. METHODS: Electron microscopy was used to analyze and measure the concentration of asbestos fibers in a series of 47 autopsies at the Asbest Town Hospital. Work histories were obtained from pathology reports and employment records. RESULTS: In 24 chrysotile miners, millers, and product manufacturers, the pulmonary concentrations of retained fibers (over 1 microm in length) were 0. 8-50.6 million f/g for chrysotile, and < 0.1-1.9 million f/g for amphiboles (tremolite and anthophyllite). The concentrations were lower in 23 persons without any known occupational contact with asbestos; 0.1-14.6 million f/g for chrysotile, and < 0.1-0.7 million f/g for amphiboles. On average, 90% of all inorganic fibers were chrysotile, and 5% tremolite/anthophyllite. No amosite or crocidolite fibers were detected in any of the samples. CONCLUSIONS: The mean and range of pulmonary chrysotile concentrations were about the same as reported previously from the Canadian mining and milling industry. In the Russian samples, the mean concentration of tremolite fibers were less by at least one order of magnitude. Occupational contact was the most important source of asbestos exposure.

Adolescent↗

Size and shape of airborne asbestos fibres in mines and mills.

There is increasing evidence that fibre size and shape play an important part in the production of health effects related to asbestos. The dimensions of airborne fibres collected at various stages of fibre processing in three mines and six mills producing three types of asbestos were measured using phase contrast light microscopy and transmission electron microscopy. Airborne fibres of different asbestos types had appreciably different size and shape distributions. For a given asbestos type, fibres collected at different stages of processing differed in their size distributions but the differences were considerably less than between fibre types. Most of the airborne fibres to which miners and millers were exposed were short and thin and thus respirable. The physical properties which best differentiated crocidolite fibres from other types of asbestos and which had higher values determined for crocidolite fibres than those obtained for the other types, were median aspect ratio and the proportion of long thin fibres--that is, fibres less than or equal to 0.2 micron in diameter and greater than 5 micron in length as the percentage of total fibres. The median true diameter of amosite fibres was about four and three times higher than the median true diameters of chrysotile and crocidolite fibers respectively. The median true length of amosite fibres was more than four and two times higher than the median true lengths of chrysotile and crocidolite fibres respectively. The observed differences in size and shape of airborne fibres have important implications for the setting of work environmental standards and in explaining differences in health risks associated with different types of fibre.

Air↗

Enhanced retention of asbestos fibers in the airways of human smokers.

To determine whether cigarette smoke increases the pulmonary retention of asbestos, we compared the asbestos-fiber burden in the airway mucosa of six cigarette smokers who had received heavy occupational asbestos exposure with that in a group of six subjects with similar exposure who were never smokers. The groups were matched in terms of age, sex, years of exposure, and mean parenchymal amosite burden. We found that the concentration of amosite in airway mucosa was significantly elevated (by approximately sixfold) in smokers (p < 0.02). Chrysotile parenchymal burdens were statistically similar in both groups, but the chrysotile airway burden was again higher (by approximately 50-fold) in smokers (p < 0.006). There were no differences in airway or parenchymal tremolite burdens between the two groups. Fibers of all three types of asbestos recovered from the airway mucosa or parenchyma of smokers were shorter than fibers recovered from nonsmokers, an observation in accord with experimental data suggesting that cigarette smoke leads to retention of shorter fibers. These findings indicate that cigarette smoking causes enhanced accumulation of both amosite and chrysotile in the airway mucosa. This process may play a role in potentiating the pathologic effects of asbestos.

Aged↗

Correlation between lung fibre content and disease in East London asbestos factory workers.

The lungs from 36 former workers at an East London asbestos factory dying of asbestos-related disease were compared with lung tissue from 56 matched control patients operated on in East London for carcinoma of the lung. The severity of asbestosis and the presence of pulmonary carcinoma or mesothelioma of the pleura or peritoneum were correlated with an asbestos exposure index and with the type and amount of mineral fibre of the lungs. Asbestosis was associated with far heavier fibre burdens than mesothelioma. Moderate or severe asbestosis was more common among those with carcinoma of the lung than in those with mesothelial tumours. Crocidolite and amosite asbestos were strongly associated with asbestosis, carcinoma of the lung and mesothelial tumours, whereas no such correlation was evident with chrysotile or mullite. It is suggested that greater emphasis should be placed on the biological differences between amphibole and serpentine asbestos fibre.

Aluminum Silicates↗

[A study of DNA damage induced by asbestos fibers in vitro].

The results of our in vitro study showed that Rhodesia chrysotile, X. K. chrysotile, UICC chrysotile, crocidolite and amosite could cause damage to calf thymus DNA by inducing the production of 8-hydroxy-2'-deoxyguanosine (8-OH-dG). After adding H2O2 and/or FeSO4, the production of 8-OH-dG, induced by asbestos fibers was significantly increased. The fiber of UICC crocidolite has the most untoward effect, that of UICC amosite comes next, and the three chrysotile fibers are the weakest ones. The effect of asbestos fibers on the production of 8-OH-dG has some relationship with hydroxy free radical and the type of asbestos. It is suggested that asbestos fibers could induce DNA point mutation through A.T and G.C transversion by the production of 8-OH-dG, which is related with the carcinogenesis of asbestos.

8-Hydroxy-2'-Deoxyguanosine↗

[First intercalibration test of diffractometric measurements of asbestos in National Italian laboratories].

The Ministry of Health established by law (D.M. 14/5/96) minimum requirements for laboratories intending to perform asbestos analyses, and identified the central facilities that are to coordinate the future quality control programme (based on the kind of techniques used), to which the laboratories must refer in order to continue to operate in the "asbestos" field. Before initiating the quality control programme for the gravimetric technique based on X-ray diffraction measurement, the central facilities decided to carry out a pilot test in a group of sample laboratories in order to assess the current situation in Italy and identify the main problems involved in implementing the programme. In fact, up to the present, no standardized method for the diffractometric measurement of asbestos exists in Italy, so that the various laboratories use different procedures and reference standards. In the pilot test, a group of 15 national laboratories with proven experience performed diffractometric measurements on 3 samples each containing one of the 3 commercial forms of asbestos (chrysotile, crocidolite and amosite). Besides the final result consisting of the percentage by weight compared to the whole sample, information was requested on the measurement procedure and on the reference standards used. The results, although they do not permit definite conclusions to be drawn due to their small number, do provide information that will be of relevance to the organisation of the future quality control programme. Analysis of the data appear to show that neither the measurement procedure used nor the type of asbestos influence the accuracy of the results. The main source of variability and of deviation from the true values seemed instead to depend on the type of standards used and on compatibility, in terms of particle size and comminution technique, between these standards and the samples analyzed.

Asbestos↗

Mesothelioma, asbestos, and reported history of cancer in first-degree relatives.

BACKGROUND: Although malignant mesothelioma is known to be strongly related to asbestos exposure, its relationship to familial factors is unclear. METHODS: We compared reported histories of cancer in first-degree relatives, obtained from telephone interviews with the next-of-kin of 196 patients who had a pathologic diagnosis of mesothelioma, and with those from 511 decreased controls. RESULTS: Among men exposed to asbestos, we found a statistically significant twofold elevation in the risk of mesothelioma for patients reporting cancer in two or more first-degree relatives. We found no significant elevation in women or among the small number of men without asbestos exposure. The next-of-kin of three patients (but no controls) reported a possible mesothelioma in a first-degree relative; asbestos exposure could not be ruled out in those relatives. Associations of asbestos with pleural mesothelioma were stronger among men with a reported family history of cancer than men without, although no statistical evidence of an interaction was detected. CONCLUSIONS: These results provide suggestive, but limited, evidence that a family history of cancer may be a risk factor for mesothelioma, or may indicate an increased susceptibility to mesothelioma given asbestos exposure.

Asbestos↗

A study of lung cancer mortality in asbestos workers: Doll, 1955.

Between 1935 and 1953, a series of publications appeared in England, Germany and America reporting cases of lung cancer amongst asbestos workers. As early as 1943, the German scientific consensus was that the evidence was strong enough to deem the association to be causal. On reviewing a more extensive bibliography, this view was shared by an American cancer expert. The results of industry sponsored experiments, in which lung tumors had been induced in mice by asbestos, were circulated in confidence to its scientists, but being unpublished were unknown to the general scientific community. There were also cancer mortality data recorded for populations of exposed asbestos workers, but these were confidential and remained to be analyzed. To deal with the persistent allegations of a lung cancer hazard, in 1953 Dr. Richard Doll was asked by Turner Brothers Asbestos ("the Company"), whose in-house analyses had been reassuring, to study the mortality data of a group of its workers. Despite the limitations of the data, Doll convincingly demonstrated so substantial an excess of lung-cancer in heavily exposed long-term asbestos workers as to overcome honest doubt. Despite determined attempts made to dissuade them, Doll and the editor of the journal to which he submitted his paper, courageously went ahead and published the paper. Industry overestimated the harm that publication of the paper would do to their immediate interests. It produced so profound a lack of sense of urgency, that legislation addressed to the control of lung cancer specifically had to wait 20 years, and asbestos workers contracting it were to wait 25 years, before they might be considered for compensation, and even then, only under extremely limiting conditions.

Animals↗