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Biomedical subjects

M Kuschner

Publications and source records attributed to M Kuschner.

At least 19 recordsLinked to original sources
PubMed1999

Olfaction and symptoms in the multiple chemical sensitivities syndrome.

Whereas most idiosyncratic environmental sensitivity complaints do not fit known diagnoses, the multiple chemical sensitivities syndrome (MCS) is an extreme presentation that has defined diagnostic criteria. MCS symptomatics claim that they acquired a sensitized state as the result of a chemical exposure, usually to a solvent or pesticide, but not to a fragrance. Before this exposure, they did not experience symptoms. Following sensitization, symptoms increasing in number and severity with time are attributed by the MCS symptomatic to various exposures that are innocuous to most individuals. Although phenomenological studies have provided no evidence that particular odors elicit MCS symptoms, low levels of fragrances and perfumes are frequently associated with the reporting of MCS symptoms. This evaluation examines proposed mechanisms by which odorants and fragrances might cause either sensitization or elicitation of MCS symptoms, including altered odor sensitivity, primary irritancy or irritancy-induced upper airway reactivity, neurogenic switching of trigeminal irritancy signals, time-dependent sensitization and limbic kindling, CNS toxicity, and various psychiatric conditions. In no case was there persuasive evidence that any olfactory mechanism involving fragrance underlies either induction of a sensitized state or the triggering of MCS symptoms. Fragrances and other odorants could, however, be associated with symptoms as claimed by MCS symptomatics, because they are recognizable stimuli, but fragrance has not been demonstrated to be causal in the usual sense.

Environmental Exposure↗
PubMed1996

A comparison between the localization of lung tumors in uranium miners and in nonminers from 1947 to 1991.

BACKGROUND: Lung cancer was noted to be increased in cigarette smoking miners and nonminers. Carcinogen particulates deposit differentially in the central, middle, and peripheral zones of the bronchial tree depending on the size of the particle. The object of this study was to evaluate the incidence of tumors; their cell types; and the relationship of particulate size to their position in the bronchial tree. METHODS: Tumor position in the bronchial tree was studied for a cohort of 467 uranium miners and 311 nonminers with lung cancer. RESULTS: An examination of all histologic subtypes showed that the proportion of lung cancers in the central zone was significantly greater in miners than in nonminers presumably due to the deposition of radon decay products attached to the silica dust particles. The higher percentage of central tumors in the miners was primarily due to the distribution of a greater proportion of squamous cell and small-cell tumors. The ratio of 0.75 for the central to middle and peripheral location for adenocarcinomas was much lower than for squamous cell and small-cell carcinomas with ratios of 1.4 and 7.3, respectively. In the mining cohort, there were ten times as many small-cell tumors in the central area as in the middle and peripheral regions, whereas, for the nonminers there were only five times as as many centrally located small-cell tumors as middle and peripheral (chi square is 7.0 degrees, P < 0.01). These data suggest that radon may be deposited preferentially to the central region of the lungs in uranium miners. CONCLUSIONS: Based on our observations of the differential positions of lung tumors in the bronchial tree for miners and nonminers and previous studies by others regarding size-dependent deposition of particulates in the bronchial tree, it is concluded that inhaled dust, radon, and cigarette smoke combine to form large particulates that deposit in the central bronchial tree. Filtered cigarette smoke or other small carcinogens from smaller particulates that deposit more peripherally.

Bronchial Neoplasms↗
PubMed1996

Analysis of fatal pulmonary hantaviral infection in New York by reverse transcriptase in situ polymerase chain reaction.

The purpose of this study was to analyze the histological distribution of polymerase chain reaction (PCR)-amplified hantaviral cDNA in three cases of fatal hantaviral infection that occurred 2 years ago in Long Island, NY. The three otherwise healthy patients had a rapid death characterized by fever and pulmonary failure and were identified from the autopsy files at University Hospital, Stony Brook. Six autopsy controls with either no pulmonary disease (three) or fatal pneumonitis of known etiology (three) were also studied. PCR-amplified hantaviral cDNA was detected in the lung tissue of the three cases and none of the six controls using the reverse transcriptase in situ PCR technique. In the positive cases, viral RNA was detected in approximately 20% of pneumocytes and alveolar endothelial cells as determined with a consensus and Four Corners-specific primer pair. Infected endothelial cells were identified in a wide variety of other sites, but at rates much lower than in the lungs. The selective localization of the viral RNA in many pneumocytes and pulmonary endothelial cells using a highly sensitive PCR-based test demonstrates a correlation between direct viral infection in the lung and the disease process.

Aged↗
PubMed1994

Asbestos in the air of public buildings: a public health risk?

The Environmental Health and Safety Council of the American Health Foundation has examined current estimates of cancer risks associated with the presence of asbestos-containing materials (ACM) in public buildings. The Council finds that even complete removal of asbestos from all of these buildings will provide no measurable benefit to public health. The removal of nonfriable ACM only can be postulated to protect the public against a small hypothetical risk that cannot be measured epidemiologically. Moreover, examination of the assumptions used in the risk assessment calculations leads to the conclusion that these small calculated risks are likely to represent overestimates. In recent surveys, the measured asbestos levels in indoor air cast some doubt on whether occupant exposure to asbestos levels are contributed to significantly by ACM even when some of the material is friable or in bad condition. Furthermore, the models used for cancer risk estimates assume no threshold level for cancer and conclude that any exposure is carcinogenic. This may be unjustified in light of information on the mechanisms for some asbestos-caused disease. Based on the best available data, it is very unlikely that cancer will result from indoor asbestos exposure, especially where ACM is well maintained.

Air Pollution, Indoor↗
PubMed1988

Relationship of radioactive radon daughters and cigarette smoking in the genesis of lung cancer in uranium miners.

This article documents the study of 383 cases of lung cancer in uranium miners and presents for the first time the relationship of radioactive radon gas and cigarette smoking. There is evidence that alpha radiation from radon gas at exposure levels above 465 working level months (WLM) is a strong contributor to the development of lung cancer. Cigarette smoking plays the most significant role in causing lung tumor; this is also noticed in nonminers who smoke cigarettes. A synergistic or additive effect of these two carcinogens is strongly suggested. The data indicate that small cell tumors develop in younger nonsmoking miners exposed to radon levels above 465 WLM. Lung cancers develop in smoking miners at lower levels of radon exposure than in nonsmoking miners. Based on an average mining experience of 15 years, there is substantial evidence that the present maximum allowable limit of 0.3 working levels (WL), or 4 working level months (WLM) per year, is safe, representing a margin of safety of approximately 10:1. Furthermore, a comparison of these data with the radon levels in some homes, averaging in the neighborhood of 0.025 WL, would indicate that health risks at these levels are negligible. It is suggested that 20 picocuries/liter, which equals 0.10 WL, be the maximum allowable level in homes.

Adult↗
PubMed1986

Contribution of environmental fibers to respiratory cancer.

This article reviews studies of the carcinogenicity of mineral fibers, notably asbestos, and presents seven major recommendations for further research. Mineral fibers represent the greatest cause--after cigarette smoke--of respiratory cancer due to air pollutants. Past asbestos exposure may currently account for 2000 mesothelioma deaths per year and 4000 to 6000 lung cancer deaths per year. All major commercial types of asbestos (crocidolite, amosite, and chrysotile) can cause each of the major asbestos-related respiratory diseases. Lung cancers in asbestos-exposed individuals probably do not have a different distribution of histological types from that of non-asbestos-related lung cancers. Nonoccupational exposures are likely to be associated with malignant disease outcomes qualitatively similar to those associated with occupational exposures. Further investigations of fibers are needed to characterize the relationships among physicochemical properties, patterns of migration and clearance, dose, and adverse health effects. Transmission electron microscopy has been found to be the preferred method of analysis of environmental fibers. Relations among time factors (e.g., age at first exposure), dose, and risk for adverse health effects require analyses of existing and new epidemiologic studies of exposed cohorts. Concomitant exposure, behavioral factors, and host factors affecting susceptibility to asbestos should be identified.

Air Pollutants↗
PubMed1982

Gaseous formaldehyde and hydrogen chloride induction of nasal cancer in the rat.

The carcinogenic response to the combined and separate exposures to formaldehyde (HCHO) and hydrochloric acid (HCl) was investigated in male inbred SD rats. The rats were exposed to gaseous HCHO, 14 ppm, and HCl, 10 ppm, in two experiments. In one experiment the gases were premixed at high concentrations before being diluted in the exposure chamber air to maximize the formation of the carcinogen bis(chloromethyl)ether (BCME). In the second experiment exposure was repeated to HCl and HCHO premixed at high concentrations, and not premixed (to minimize BCME formation), as well as to HCHO alone and HCl alone. The second experiment is being reported on at an interim stage. HCHO alone induced squamous carcinomas of the nasal cavity as did the combined exposures to HCHO and HCl. No carcinogenic response was observed with HCl alone. HCHO accounted for most, if not all, of the carcinogenic activity of the mixture of HCHO-HCl.

Animals↗
PubMed1981

Arsenic exposure in a copper smelter as related to histological type of lung cancer.

Tissue samples from lung cancer patients who had worked at a copper smelter and from controls were collected and classified by a panel of pathologists: 38% of the cancers were found to be adenocarcinomas, compared to 12% among the controls, a statistically significant difference (p less than 0.05). The predominance of adenocarcinomas was associated with arsenic exposure. This finding is not consistent with Kreyberg's hypothesis that small-cell undifferentiated and epidermoid carcinomas are the only type that increase in response to inhaled carcinogens [1962].

Aged↗
PubMed1981

The carcinogenicity of beryllium.

Beryllium, some of its alloys, and a variety of its compounds have induced malignant tumors of the lung and osteogenic sarcoma in experimental animals. Three animal species, monkeys, rabbits, and rats, have been shown to be susceptible. Beryllium induces morphological transformation in mammalian cells and enhances viral transformation of mammalian cells. It has been shown to decrease fidelity of DNA synthesis. It has been recognized that exposure to compounds of this metal will, in some individuals, result in a chronic granulomatous disease of the lung. A series of overlapping recent human epidemiological studies have been suggestive of an increase in the incidence of lung cancer in populations occupationally exposed to beryllium. Such studies, together with animal and in vitro studies, argue for the strong presumption of a carcinogenic hazard to man in occupational beryllium exposures.

Animals↗
PubMed1980

Inhalation carcinogenicity of epichlorohydrin in noninbred Sprague-Dawley rats.

Inhalation exposure experiments with the direct-acting alkylating agent epichlorohydrin (ECH) were done on noninbred male Sprague-Dawley rats. Single 6-hour exposure to ECH and follow-up for 14 days showed the median lethal concentration to be about 360 ppm. Further inhalation experiments were done with 6-hour exposure 5 days/week. A short-term 30-exposure regimen with 100 ppm ECH produced malignant squamous cell carcinomas of the nasal cavity in 15 of 140 rats and respiratory tract papillomas in 3 rats. Among 100 rats, lifetime exposure to 30 ppm yielded 1 malignant squamous carcinoma of the nasal cavity plus 1 nasal papilloma. No nasal or respiratory tract tumors were produced by lifetime exposure of 100 rats to 10 ppm. As controls, 100 air-treated and 50 untreated rats were used. A dose-rate effect was observed for ECH inasmuch as 30-day exposure to 100 ppm (3,000 ppm-days) produced 15 cancers in comparison to the 1 cancer from the lifetime exposure to 30 ppm (8,700 ppm-days) and no cancers from lifetime exposure to 10 ppm (2,500 ppm-days).

Animals↗
PubMed1980

Experimental approaches for exposure to sized glass fibers.

A number of studies have shown that glass fibers induce both malignant mesothelioma and fibrosis in rats and that these reactions may be primarily a function of the physical properties of the fiber. However, these studies were carried out with fibers having broad size distributions and used methods of administration which bear little resemblance to the way man is exposed. To better characterize the health effects of glass fibers, techniques have been developed to expose rats to glass fibers of defined sizes by intratracheal instillation of aqueous suspensions and by "nose only" inhalation exposure, and to determine the deposition, translocation, and ultimate fate of these fibers in the rat. The fibers have known size distributions with geometric mean diameters of 1.5 micrometers (sigma g = 1.1) and lengths of either 5 micrometers (sigma g = 1.49) or 60 micrometers (sigma g = 3.76). The fibers have been activated with neutron irradiation. Of the several resulting radionuclides, 65Zn appeared to be the most suitable for long-term clearance studies by use of in vivo whole body radioassay techniques. A fluidized bed aerosol generator has been developed to expose rats by "nose only" inhalation to approximately 500 fibers/cm3. The generator and exposure system permits reuse of fibers which pass through the exposure chamber and produces no significant alteration of the fiber size distribution. Rats were exposed by intratracheal instillations to 20 mg of the longer fibers and to equal numbers (2 mg) and equal mass (20 mg) of the shorter fibers. Through approximately 19 weeks little difference was observed in the whole rat clearance rate of long versus short fibers in the initial exposure group. Histopathology, however, showed differences at this time with the short fibers apparently successfully phagocytized by alveolar macrophages and cleared to the lymph nodes, while the long fibers were not.

Aerosols↗