Academic literature on the topic 'Naturally Occurring Asbestos'

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Journal articles on the topic "Naturally Occurring Asbestos"

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Yoon, Sungjun, Kyubong Yeom, Yongun Kim, Byungno Park, Jaebong Park, Hyesu Kim, Hyeonyi Jeong, and Yul Roh. "Management of Naturally Occurring Asbestos Area in Republic of Korea." Environmental and Engineering Geoscience 26, no. 1 (February 20, 2020): 79–87. http://dx.doi.org/10.2113/eeg-2287.

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ABSTRACT The Republic of Korea Government has adopted a whole-of-government approach in the management of naturally occurring asbestos (NOA) through a nationwide asbestos management plan. Regional and detailed mapping, and examination of NOA effects are still ongoing for NOA management by indoor air, noise and asbestos management division, Ministry of Environment. Plans by the Korea Rail Network Authority are under way to rebuild the Janghang double-track railway. The proposed Jannghang double-track railway route is through an area of high NOA probability that has serpentine and ultramafic rock. Chrysotile, tremolite, and actinolite asbestos were among the rocks identified within the project site (initial planning line and the operational design line). The level of asbestos in most soils was low (≤0.25 percent), while some soils contained 0.75 percent asbestos. Monitoring and analyses of air quality revealed below 0.01 fibers per cm3 (f/cc). However, there were no traces of asbestos detected in the groundwater and stream water. Despite the low asbestos content of the soil and rock, the disturbance of NOA-containing soils and rocks during railway construction could trigger the release of asbestos fibers into the air. NOA mitigation plans and measures are necessary for workers and residents during the construction of the railway.
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Cagnard, Florence, and Didier Lahondère. "Naturally Occurring Asbestos in France: Geological Mapping, Mineral Characterization, and Technical Developments." Environmental and Engineering Geoscience 26, no. 1 (February 20, 2020): 53–59. http://dx.doi.org/10.2113/eeg-2277.

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ABSTRACT In France, asbestos was banned by national decree (no. 96-1133) in 1996. The regulatory texts and standards adopted to implement this ban are concerned primarily with asbestos-containing manufactured products and are difficult to apply to asbestos-bearing natural materials (i.e., rocks and soils). Considering problems related to asbestos-bearing natural materials, the French Ministry of Ecology, Sustainable Development, and Energy has mandated the French Geological Survey to map locations where asbestos-bearing rocks are found. Mapping was prioritized to geological domains where naturally occurring asbestos (NOA) was predictable (e.g., the Western Alps and Corsica). These studies integrated field expertise, sampling, and laboratory analysis data to characterize the potential of geological units to contain NOA. Additionally, studies were conducted on geological formations exploited to produce aggregates. These studies were focused on quarries excavating massive, basic or ultrabasic rocks likely to contain NOA and quarries mining alluvium likely to contain asbestos-bearing rock pebbles. These studies highlight the difficulty of establishing robust analytical procedures for natural materials. The distinction between cleavage fragments (resulting from the fragmentation of non-asbestos particles) and proper asbestos fibers is particularly problematic for laboratories. Thus, a recent study by the National Agency for Health Safety, Food, Environment, and Work recommends applying the asbestos regulation to elongated mineral particles (length/depth > 3:1, length > 5 μm, depth < 3 μm) with chemical composition corresponding to one of the five regulated amphibole species regardless of their mode of crystallization (asbestiform or non-asbestiform). The upcoming regulatory changes are part of a decree published in 2017, including the prior identification of asbestos in natural soils or rocks likely to be impacted by ground-disturbing construction activities. Specific protocols will be defined for sampling, analysis, and characterization of natural materials that may contain asbestos.
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Harper, Martin. "10th Anniversary Critical Review: Naturally occurring asbestos." Journal of Environmental Monitoring 10, no. 12 (2008): 1394. http://dx.doi.org/10.1039/b810541n.

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Pathak, Arvind, Manbir Giri, Bishnu Pokhrel, and Manoj Nidhi Wagle. "Identification of Asbestos Content in Bulk Materials Imported in Nepal." Scientific World 13, no. 13 (August 4, 2020): 5–7. http://dx.doi.org/10.3126/sw.v13i13.30481.

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The bulk materials include the construction materials such as plaster sand gravel and cement as well as raw materials. Asbestos is the naturally occurring magnesium silicate mineral fibers which has high tensile strength, flexibility and resistance to chemicals, high temperature and stress; this is why it has been considered and used in bulk materials. These mineral fibers are needle shaped and can stick to lung tissue when inhaled and cause inflammation and serious health problems such as asbestosis, mesothelioma and lung cancer or internal fibrosis. It can be detected by simple microscopic method using mineral acid and heat treatment. The method would help in quality analysis of asbestos fiber and save from asbestos induced disease and to develop alternative materials of asbestos fiber material.
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Bloise, Andrea, Rosalda Punturo, Robert Kusiorowski, and Dolores Pereira Gómez. "Editorial for Special Issue “Mineral Fibres”." Fibers 7, no. 6 (June 13, 2019): 54. http://dx.doi.org/10.3390/fib7060054.

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Pierdzig, Stefan. "Regulations Concerning Naturally Occurring Asbestos (NOA) in Germany—Testing Procedures for Asbestos." Environmental and Engineering Geoscience 26, no. 1 (February 20, 2020): 67–71. http://dx.doi.org/10.2113/eeg-2278.

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ABSTRACT In Germany, potential asbestos-containing rocks are used as raw materials for a number of engineering applications. These rocks are ultrabasites (dunite, harzburgite), igneous rocks (basalt, gabbro, norite), and metasomatic or metamorphic rocks like talcum, greenschist and amphibolite. Based on the German Gefahrstoffverordung (Hazardous Substances Ordinance), regulatory statutes exist for operations using these rocks and resultant composites and products. The authorities state that in Germany no natural rocks exist with more than 0.1 mass-% of one of the six regulated asbestos minerals. But it is well known that there are rocks with a high modal concentration of these minerals with a non-asbestiform, columnar to prismatic habitus. Under mechanical stress during handling, they can lead to fibrous cleavage fragments, which conform to the World Health Organization (WHO) “respirable asbestos fiber” definition. In view of this fact, the regulations changed in 2009, with revision of the Technical Rules for Hazardous Substances (TRGS) 517: any fibrous asbestos particles, regardless of whether or not they represent naturally occurring asbestos or are of cleavage origin, are evaluated for potential hazards associated with handling of these rocks. If the WHO fiber concentration is <0.1 mass-%, rocks and products can be used and re-used under protective measures. At concentrations >0.1 mass-%, the material is considered hazardous waste. These regulations apply to many industrial sectors that exploit and process rocks, using them in road building and track construction and when they are recycled. Analysis (by scanning electron microscopy, SEM/energy dispersive x-ray spectroscopy, EDS) to determine the asbestos concentration of rocks, gravels, or dusts is carried out in the <100-µm, grain-size fraction produced by sieving or grinding. The results provide a representation of a worst-case examination of the air quality during mechanical treatment of these materials. Workplace monitoring is done by air sampling to survey an exposure limit of 10,000 fibers/m3 of air (0.01 f/cc).
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Bloise, Andrea, Claudia Ricchiuti, Eugenia Giorno, Ilaria Fuoco, Patrizia Zumpano, Domenico Miriello, Carmine Apollaro, Alessandra Crispini, Rosanna De Rosa, and Rosalda Punturo. "Assessment of Naturally Occurring Asbestos in the Area of Episcopia (Lucania, Southern Italy)." Fibers 7, no. 5 (May 16, 2019): 45. http://dx.doi.org/10.3390/fib7050045.

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Over the last few years, the risk to human health related to asbestos fiber exposure has been widely demonstrated by many studies. Serpentinites are the main rocks associated with naturally occurring asbestos (NOA). In order to investigate the presence of NOA, a mineralogical study was conducted on eleven serpentinite samples collected nearby the village of Episcopia (Lucania, Southern Italy). Various analytical techniques such as X-ray powder diffraction (XRPD), scanning electron microscopy combined with energy dispersive spectrometry (SEM-EDS) and derivative thermogravimetry (DTG) were used to determine the occurrence of asbestos minerals and to make morphological observations. Results pointed out that all of the samples contain asbestos minerals (e.g., tremolite, actinolite and chrysotile). Moreover, it was observed that both natural processes and human activity may disturb NOA-bearing outcrops and provoke the formation of potentially inhalable airborne dust causing the release of asbestos fibers into the environment, thereby increasing the risk to human health. For this reason, our study aims to highlight the requirement of a natural asbestos survey and periodic update in the area.
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Epting, Shane. "Affordable Housing in Regions with Naturally Occurring Asbestos." Environmental Justice 13, no. 1 (February 1, 2020): 15–20. http://dx.doi.org/10.1089/env.2019.0027.

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Baietto, Oliviero, and Paola Marini. "Naturally occurring asbestos: Validation of PCOM quantitative determination." Resources Policy 59 (December 2018): 44–49. http://dx.doi.org/10.1016/j.resourpol.2018.06.006.

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Lee, R. J., B. R. Strohmeier, K. L. Bunker, and D. R. Van Orden. "Naturally occurring asbestos—A recurring public policy challenge." Journal of Hazardous Materials 153, no. 1-2 (May 2008): 1–21. http://dx.doi.org/10.1016/j.jhazmat.2007.11.079.

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Dissertations / Theses on the topic "Naturally Occurring Asbestos"

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Holmes, Emma. "Effects of weathering on the surface and chemical properties of chrysotile asbestos : implications for management of naturally occurring asbestos and carbon dioxide sequestration in ultramafic mine tailings." Thesis, University of British Columbia, 2012. http://hdl.handle.net/2429/43615.

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This study focuses on the surface properties of chrysotile asbestos and the effects that naturally occurring acids and different environments, specifically stream and mine tailing environments, have in altering the surface chemistry. Surface reactions are likely the governing factors affecting chrysotile, both as a toxicant and as a carbon sequestration material. This information is important for concerns related to naturally occurring chrysotile asbestos in the environment and carbon dioxide sequestration in chrysotile tailings. FESEM, XRD, ATR FTIR, zeta potential, aqua regia digestion, ICP-MS, and ToF-SIMS were used to examine the bulk and surface properties of chrysotile asbestos. Oxalic acid and hydrochloric acid are effective at removing the magnesium brucite layer, and associated trace metals, and reducing the surface charge of chrysotile asbestos. Fibers treated with these acids are likely less hazardous from a human health perspective. Carbonic acid, a weaker acid, is much less effective at altering the surface properties of chrysotile. Natural weathering in stream and mine tailing environments altered the surface properties of chrysotile asbestos, but the extent remains unknown. It appears that the slow dissolution of magnesium is the rate-limiting step for the mineral carbonation process. The results of zeta potential analysis, a surface specific technique measured on a bulk sample, are supported by ToF-SIMS analysis, a very fine scale surface specific technique measuring a small area of one fiber. Zeta potential analysis is less expensive and time consuming to carry out than is ToF-SIMS and measures the surface characteristics of a larger sample which enables it to better account for the variability within a sample. Covering naturally occuring asbestos deposits with acid producing organic matter could enhace the weathering of chrysotile and likely reduce its toxicity over time, while also acting as a barrier, preventing the fibers from becoming airborne and posing an inhalation hazard. Treating chrysotile mine tailings with naturally occuring acids will release more magnesium, potentially increasing the rate of carbon sequesrtation.
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Books on the topic "Naturally Occurring Asbestos"

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California. Legislature. Senate. Committee on Health. Naturally-occurring asbestos: Who is responsible for protecting the public health? : informational hearing of the Senate Health and Environmental Quality committees. Sacramento, Calif: Senate Publications, 2005.

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Guidelines for geologic investigations of naturally occurring asbestos in California. Sacramento, CA: California Geological Survey, Resources Agency, Dept. of Conservation, State of California, 2002.

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Skinner, H. Catherine W., Malcolm Ross, and Clifford Frondel. Asbestos and Other Fibrous Materials. Oxford University Press, 1989. http://dx.doi.org/10.1093/oso/9780195039672.001.0001.

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This comprehensive sourcebook describes the chemical, physical, and mineralogical aspects of fibrous inorganic materials, both synthetic and naturally occurring. A general description of the fibrous state, the range of compounds that can adopt this form, and an overview of the characteristics unique to such materials form the backbone of the book . The authors also assess the application and use of asbestos and other fibrous materials in industry and evaluate their potential as health hazards. The information gathered here will be highly useful to medical investigators and legal professionals involved in environmental health.
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Samet, Jonathan M., and Aaron J. Cohen. Air Pollution. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780190238667.003.0017.

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A wide variety of manmade and naturally occurring air pollutants are known to cause cancer. Diverse exposures such as tobacco smoke, radionuclides (radon), chemicals (benzene, mustard gas, and volatile organic compounds), fibers (asbestos), and metals and metalloids (chromium, nickel, and arsenic) have long been classified as carcinogenic to humans. Historically, these classifications were based predominantly on high levels of exposure in occupational settings. Over the last thirty to forty years, scientific attention has focused on quantifying the adverse health effects of indoor and outdoor air pollutants at exposure levels several orders of magnitude lower than were studied initially. These include secondhand smoke, household exposure to radon, residential and environmental exposure to asbestos, soot from diesel-powered engines, ambient exposures to small particles (PM2.5), and indoor air pollution from the combustion of biomass and coal. This chapter provides an overview of recent epidemiologic studies of air pollutants and cancer.
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Book chapters on the topic "Naturally Occurring Asbestos"

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Leticia, Lescano, Locati Francisco, Marfil Silvina, Sfragulla Jorge, Bonalumi Aldo, and Maiza Pedro. "Naturally Occurring Asbestos in Argentina: A Compilation of Case Studies." In IAEG/AEG Annual Meeting Proceedings, San Francisco, California, 2018 - Volume 2, 169–74. Cham: Springer International Publishing, 2018. http://dx.doi.org/10.1007/978-3-319-93127-2_24.

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Segrave, Alan M., Federica Paglietti, and Sergio Malinconico. "Assessment of Naturally Occurring Asbestos and Cosmetic Talc: A Case Study." In Asbestos and Other Elongate Mineral Particles—New and Continuing Challenges in the 21st Century, 374–98. 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959: ASTM International, 2021. http://dx.doi.org/10.1520/stp163220210008.

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Worliczek, Elisabeth. "Naturally Occurring Asbestos: The Perception of Rocks in the Mountains of New Caledonia." In Environmental Transformations and Cultural Responses, 187–214. New York: Palgrave Macmillan US, 2017. http://dx.doi.org/10.1057/978-1-137-53349-4_8.

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Hernandez, Dan, and Bradley G. Erskine. "Analysis of Personal Exposure Monitoring Data for Naturally Occurring Asbestos at the Calaveras Dam Replacement Project, Sunol, California." In Asbestos and Other Elongate Mineral Particles—New and Continuing Challenges in the 21st Century, 137–68. 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959: ASTM International, 2021. http://dx.doi.org/10.1520/stp163220210001.

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Robinson, Chapman. "Asbestos and the lung." In Oxford Handbook of Respiratory Medicine, edited by Stephen J. Chapman, Grace V. Robinson, Rahul Shrimanker, Chris D. Turnbull, and John M. Wrightson, 123–40. Oxford University Press, 2021. http://dx.doi.org/10.1093/med/9780198837114.003.0017.

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Asbestos consists of a family of naturally occurring hydrated silicate fibres that may be subdivided into two groups: curly serpentine fibres, of which chrysotile (white) is the only fibre currently in commercial use, and straight, needle-like amphiboles, which comprise crocidolite (blue), amosite (brown), anthophyllite, tremolite, and actinolite. Fibres have a predisposition to localize to the pleura. They differ in their lung clearance kinetics and pathogenic potential; amphibole fibres clear more slowly from the lung and are more carcinogenic than chrysotile. While asbestos usage in developed countries is restricted, the use of chrysotile asbestos in developing economies continues to rise.
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Alexander, Earl B., Roger G. Coleman, Todd Keeler-Wolfe, and Susan P. Harrison. "Serpentine Land Use and Health Concerns." In Serpentine Geoecology of Western North America. Oxford University Press, 2007. http://dx.doi.org/10.1093/oso/9780195165081.003.0030.

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Soils developed from serpentine (ultramafic) substrates are noted for their meager and strange biomass. The chemical infertility is the main controlling factor in the development of plants in serpentine soils (Proctor and Woodell 1975, Kruckeberg 1984, Brooks 1987). Botanists have recognized the unusual nature of the endemic plants and this has led to preserving serpentine tracts that contain rare plant species. The evolution of plant species that are restricted to serpentine has produced remarkable adaptations to survival on serpentine substrates. Kruckeberg (1984) pointed out that the long-term habitat attrition on these rare natural serpentine ecosystems requires conservation initiatives to insure their preservation. In California, private and public land managers are required to develop environmental impact studies before disturbing tracts containing serpentine bedrock and its overlying soils (Clinkenbeard et al. 2003). The U.S. Fish and Wildlife Service (USFWS 1998) carried out a recovery plan for 28 species of plants and animals that occur exclusively or primarily on serpentine soils and grasslands in the San Francisco Bay area. The strategy was to provide detailed actions needed to achieve self-sustaining populations of endangered species so they will no longer require protection under the Endangered Species Act. Serpentine land tracts within metropolitan areas have come under closer regulation, as there is concern of releasing naturally occurring asbestos during construction disturbances. Typical examples of disturbance would be construction sites, new road construction, and quarry excavation. Of particular concern are the large amounts of dust produced in quarry operations or unpaved gravel roads consisting of crushed serpentine rock. The dust from such sites may contain airborne asbestos fibers released from the serpentine. This asbestos-bearing dust may pose a toxic threat to the construction workers and to later occupants of homes, schools, and office buildings occupying serpentine tracts. Asbestos is the blanket term for a group of naturally occurring silicate minerals that can be separated into fibers. The fibers are strong, durable, and resistant to extreme heat. Because of these qualities, asbestos has been used in industrial, maritime, automotive, scientific, and building products.
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Hillerdal, Gunnar. "Health Problems Related to Environmental Fibrous Minerals." In Geology and Health. Oxford University Press, 2003. http://dx.doi.org/10.1093/oso/9780195162042.003.0025.

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Very early in the history of mining and with the industrial applications of asbestos, it was known that a variety of mineral fibers were hazardous to health. By the 1940s, the potential risk of lung cancer, in addition to the fibrosis disorder asbestosis, one of the pneumoconioses, was described. Within twenty years, another malignant disease, mesothelioma, cancer of the tissues that surround the lung, was ascribed to asbestos exposure. It is now common knowledge that inhalation of certain mineral fibers can cause disease (Skinner et al. 1988). Because the fibers are inhaled, the lung and surrounding tissues are the primary targets, but there may be subsequent reactions in many other parts of the body. The information on disease related to fibrous materials emanates from studies of occupational environments where the dose or exposure is likely to be high and continued over long periods of time. However, it has been increasingly realized that domestic or general environmental exposure is also possible and can pose grave dangers. For a mineral fiber to be inhalable it should be less than one micron in diameter, but the length can be 10 microns or greater because the particle can align with the air stream in the bronchi and penetrate far into the lung. The ratio between length and diameter of the fiber is critical. The most dangerous fibers are very thin (one tenth of a micron in diameter or less) with a high length-diameter ratio. Another important factor is biodurability. Typically, the dangerous fibers are not broken down at all or only very slowly, with half-lives in the body of many years. They may remain in situ throughout life and can be found at autopsy. There are many varieties of fibers in the environment today, both naturally occurring and man-made. Only a few, however, fulfill the above criteria and occur in amounts where human exposure is possible. The problem fibers are collectively known as asbestos and the fibrous zeolite, erionite. There are many other fibers (Skinner et al. 1988), but their contributions to human disease are not recognized. Asbestos is not a mineralogical but a commercial term.
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Skinner, H. Catherine W., Malcolm Ross, and Clifford Frondel. "Fibrous Minerals and Synthetic Fibers." In Asbestos and Other Fibrous Materials. Oxford University Press, 1989. http://dx.doi.org/10.1093/oso/9780195039672.003.0005.

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A mineral is a naturally occurring, crystalline inorganic compound with a specific chemical composition and crystal structure. Minerals are commonly named to honor a person, to indicate the geographic area where the mineral was discovered, or to highlight some distinctive chemical, crystallographic, or physical characteristic of the substance. Each mineral sample has some obvious properties: color, shape, texture, and perhaps odor or taste. However, to determine the precise composition and crystal structure necessary to accurately identify the species, one or several of the following techniques must be employed: optical, x-ray diffraction, transmission electron microscopy and diffraction, and chemical and spectral analyses. The long history of bestowing names on minerals has provided some confusing legacies. Many mineral names end with the suffix “ite,” although not most of the common species; no standard naming practice has ever been adopted. Occasionally different names have been applied to samples of the same mineral that differ only in color or shape, but are identical to each other in chemical composition and crystal structure. These names, usually of the common rock-forming minerals, are often encountered and are therefore accepted as synonyms or as varieties of bona fide mineral species. The Fibrous Minerals list (Appendix 1) includes synonyms. A formal description of a mineral presents all the physical and chemical properties of the species. In particular, distinctive attributes that might facilitate identification are noted, and usually a chemical analysis of the first or “type” specimen on which the name was originally bestowed is included. As an example, the complete description of the mineral brucite (Mg(OH)2), as it appears in Dana’s System of Mineralogy, is presented as Appendix 3. Note the complexity of this chemically simple species and the range of information available. In the section on Habit (meaning shape or morphology) both acicular and fibrous forms are noted. The fibrous variety, which has the same composition as brucite, is commonly encountered (see Fig. 1.1D) and is known by a separate name, “nemalite.” Tables to assist in the systematic determination of a mineral species are usually based on quantitative measurements of optical properties (using either transmitted or reflected light, as appropriate) or on x-ray diffraction data.
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Conference papers on the topic "Naturally Occurring Asbestos"

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Metcalf, Rodney V., Brenda J. Buck, Brett T. McLaurin, and Jean C. Pfau. "IN DEFENSE OF THE TERM “NATURALLY-OCCURRING ASBESTOS”." In GSA Annual Meeting in Seattle, Washington, USA - 2017. Geological Society of America, 2017. http://dx.doi.org/10.1130/abs/2017am-307158.

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Buck, Brenda J., Rodney V. Metcalf, and Brett T. McLaurin. "NATURALLY-OCCURRING ASBESTOS AND INCREASED URBANIZATION IN CLARK COUNTY, NEVADA." In GSA Annual Meeting in Phoenix, Arizona, USA - 2019. Geological Society of America, 2019. http://dx.doi.org/10.1130/abs/2019am-335233.

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Buck, Brenda J., Christopher Wolfe, Aubrey Miller, James E. Lockey, Christopher P. Weis, David Weissman, Alexander Jonesi, and Patrick H. Ryan. "EXPOSURE TO NATURALLY OCCURRING ASBESTOS DUE TO OFF-ROAD VEHICLE USE." In GSA Annual Meeting in Seattle, Washington, USA - 2017. Geological Society of America, 2017. http://dx.doi.org/10.1130/abs/2017am-300260.

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Metcalf, Rodney V., and Brenda J. Buck. "NATURALLY-OCCURRING ASBESTOS AND PUBLIC HEALTH: THE IMPORTANCE OF INTERDISCIPLINARY RESEARCH." In GSA Annual Meeting in Indianapolis, Indiana, USA - 2018. Geological Society of America, 2018. http://dx.doi.org/10.1130/abs/2018am-324931.

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Gillis, Morgan, Kailee Gokey, Natalie Renkes, Ken Brown, and Mark Krekeker. "EXPLORING NATURALLY OCCURRING ASBESTOS IN ROAD SEDIMENT FROM BOULDER CITY, NEVADA." In GSA Connects 2021 in Portland, Oregon. Geological Society of America, 2021. http://dx.doi.org/10.1130/abs/2021am-365241.

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Kennedy, Elisabeth, Hannah Aird, Matthew Wagoner, Julianna McCracken, and Alonso Diaz. "POTENTIAL NATURALLY OCCURRING ASBESTOS IN METAVOLCANIC AND SERPENTINIZED ULTRAMAFIC ROCKS AROUND PARADISE, CA." In Joint 118th Annual Cordilleran/72nd Annual Rocky Mountain Section Meeting - 2022. Geological Society of America, 2022. http://dx.doi.org/10.1130/abs/2022cd-374319.

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Buck, Brenda J., Rodney V. Metcalf, David Berry, Brett T. McLaurin, Douglas Kent, Dirk Goossens, and Jed Januch. "NATURALLY OCCURRING ASBESTOS IN SOILS, SOUTHERN NEVADA: INTERPRETATIONS FOR WIND DISTRIBUTION AND HUMAN EXPOSURE." In GSA Annual Meeting in Denver, Colorado, USA - 2016. Geological Society of America, 2016. http://dx.doi.org/10.1130/abs/2016am-278831.

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Pascucci, S., S. Pignatti, C. Belviso, F. Cavalcante, and M. P. Bogliolo. "Worldview-3 and Sentinel-2 Imagery for Mapping Naturally Occurring Asbestos (NOA) in Serpentinites Rocks in Southern Italy." In IGARSS 2019 - 2019 IEEE International Geoscience and Remote Sensing Symposium. IEEE, 2019. http://dx.doi.org/10.1109/igarss.2019.8898336.

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Dobbs, Elizabeth, Katayoun Mobasher, and Joseph Hughart. "PRELIMINARY STUDY OF NATURALLY OCCURRING ASBESTOSES EXPOSURE AND ITS ADVERSE HEALTH EFFECTS IN NORTH GEORGIA USING GEOSPATIAL TECHNOLOGY." In Joint 56th Annual North-Central/ 71st Annual Southeastern Section Meeting - 2022. Geological Society of America, 2022. http://dx.doi.org/10.1130/abs/2022nc-375227.

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Reports on the topic "Naturally Occurring Asbestos"

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Athey, J. E. Naturally occurring asbestos in Alaska. Alaska Division of Geological & Geophysical Surveys, March 2019. http://dx.doi.org/10.14509/30162.

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Solie, D. N., and J. E. Athey. Preliminary evaluation of bedrock potential for naturally occurring asbestos in Alaska. Alaska Division of Geological & Geophysical Surveys, September 2015. http://dx.doi.org/10.14509/29447.

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