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      Perspectives on refractory ceramic fiber (RCF) carcinogenicity: comparisons with other fibers*

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          Abstract

          In 2011, SCOEL classified RCF as a secondary genotoxic carcinogen and supported a practical threshold. Inflammation was considered the predominant manifestation of RCF toxicity. Intrapleural and intraperitoneal implantation induced mesotheliomas and sarcomas in laboratory animals. Chronic nose-only inhalation bioassays indicated that RCF exposure in rats increased the incidence of lung cancer and similar exposures resulted in mesothelioma in hamsters, but these studies may have been compromised by overload. Epidemiological studies in the US and Europe showed an association between exposure and prevalence of respiratory symptoms and pleural plaques, but no interstitial fibrosis, mesotheliomas, or increased numbers of lung tumors were observed. As the latency of asbestos induced mesotheliomas can be up to 50 years, the relationship between RCF exposure and respiratory malignances has not been fully determined. Nonetheless, it is possible to offer useful perspectives. RCF and rock wool have similar airborne fiber dimensions and biopersistence. Therefore, it is likely that these fibers have similar toxicology. Traditional rock wool has been the subject of numerous cohort and case control studies. For rock wool, IARC ( 2002) concluded that the epidemiological studies did not provide evidence of carcinogenicity. Based on analogies with rock wool (read across), it is reasonable to believe that increases in lung cancer or any mesotheliomas are unlikely to be found in the RCF-exposed cohort. RCF producers have developed a product stewardship program to measure and control fiber concentrations and to further understand the health status of their workers.

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          Principles for characterizing the potential human health effects from exposure to nanomaterials: elements of a screening strategy

          The rapid proliferation of many different engineered nanomaterials (defined as materials designed and produced to have structural features with at least one dimension of 100 nanometers or less) presents a dilemma to regulators regarding hazard identification. The International Life Sciences Institute Research Foundation/Risk Science Institute convened an expert working group to develop a screening strategy for the hazard identification of engineered nanomaterials. The working group report presents the elements of a screening strategy rather than a detailed testing protocol. Based on an evaluation of the limited data currently available, the report presents a broad data gathering strategy applicable to this early stage in the development of a risk assessment process for nanomaterials. Oral, dermal, inhalation, and injection routes of exposure are included recognizing that, depending on use patterns, exposure to nanomaterials may occur by any of these routes. The three key elements of the toxicity screening strategy are: Physicochemical Characteristics, In Vitro Assays (cellular and non-cellular), and In Vivo Assays. There is a strong likelihood that biological activity of nanoparticles will depend on physicochemical parameters not routinely considered in toxicity screening studies. Physicochemical properties that may be important in understanding the toxic effects of test materials include particle size and size distribution, agglomeration state, shape, crystal structure, chemical composition, surface area, surface chemistry, surface charge, and porosity. In vitro techniques allow specific biological and mechanistic pathways to be isolated and tested under controlled conditions, in ways that are not feasible in in vivo tests. Tests are suggested for portal-of-entry toxicity for lungs, skin, and the mucosal membranes, and target organ toxicity for endothelium, blood, spleen, liver, nervous system, heart, and kidney. Non-cellular assessment of nanoparticle durability, protein interactions, complement activation, and pro-oxidant activity is also considered. Tier 1 in vivo assays are proposed for pulmonary, oral, skin and injection exposures, and Tier 2 evaluations for pulmonary exposures are also proposed. Tier 1 evaluations include markers of inflammation, oxidant stress, and cell proliferation in portal-of-entry and selected remote organs and tissues. Tier 2 evaluations for pulmonary exposures could include deposition, translocation, and toxicokinetics and biopersistence studies; effects of multiple exposures; potential effects on the reproductive system, placenta, and fetus; alternative animal models; and mechanistic studies.
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            Length-dependent retention of carbon nanotubes in the pleural space of mice initiates sustained inflammation and progressive fibrosis on the parietal pleura.

            The fibrous shape of carbon nanotubes (CNTs) raises concern that they may pose an asbestos-like inhalation hazard, leading to the development of diseases, especially mesothelioma. Direct instillation of long and short CNTs into the pleural cavity, the site of mesothelioma development, produced asbestos-like length-dependent responses. The response to long CNTs and long asbestos was characterized by acute inflammation, leading to progressive fibrosis on the parietal pleura, where stomata of strictly defined size limit the egress of long, but not short, fibers. This was confirmed by demonstrating clearance of short, but not long, CNT and nickel nanowires and by visualizing the migration of short CNTs from the pleural space by single-photon emission computed tomographic imaging. Our data confirm the hypothesis that, although a proportion of all deposited particles passes through the pleura, the pathogenicity of long CNTs and other fibers arises as a result of length-dependent retention at the stomata on the parietal pleura. Copyright © 2011 American Society for Investigative Pathology. Published by Elsevier Inc. All rights reserved.
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              Cell size of alveolar macrophages: an interspecies comparison.

              Alveolar macrophages (AM) play a critical role in the removal of inhaled particles or fibers from the lung. Species differences in AM size may affect the number and size range of particles/fibers that can be actually phagocytized and cleared by AM. The purpose of this study was to compare the cell size of rat, hamster, monkey, and human AM by selective flow cytometric analysis of cell volume. Resident AM from CD rats, Syrian golden hamsters, cynomolgus monkeys, and nonsmoking, healthy human volunteers were harvested by standard bronchoalveolar lavage procedures. Morphometric analysis of AM was performed using a flow cytometer that generates volume signals based on the Coulter-type measurement of electrical resistance. We found that hamster and rat AM had diameters of 13.6 +/- 0.4 microns (n = 8) and 13.1 +/- 0.2 microns (n = 12), respectively. Comparatively, the AM from monkeys (15.3 +/- 0.5 microns, n = 7) and human volunteers (21.2 +/- 0.3 microns, n = 10) were larger than those from rats and hamsters. The AM from humans were significantly larger (p < 0.05) than those from all other species studied, corresponding to a 4-fold larger cell volume of human AM (4990 +/- 174 microns 3) compared to hamster (1328 +/- 123 microns 3) and rat (1166 +/- 42 microns 3) AM. In summary, we have found marked species differences in the cell size of AM. We suggest that the number and size range of particles/fibers that can be phagocytized and cleared by AM may differ among species due to inherent or acquired species differences in AM cell size.
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                Author and article information

                Journal
                Inhal Toxicol
                Inhal Toxicol
                IHT
                Inhalation Toxicology
                Informa Healthcare USA, Inc.
                0895-8378
                1091-7691
                November 2014
                29 September 2014
                : 26
                : 13
                : 789-810
                Affiliations
                1Institute of Molecular Pharmacology and Toxicology, Technical University MunichGermany
                2Department of Medicine and Environmental Medicine, University of Rochester School of Medicine and Dentistry Rochester, NYUSA
                3Everest Consulting Associates Cranbury, NJUSA
                Author notes

                *Based in part on a talk presented at the International Conference “Advances and Controversies in Fibre Toxicology” at CMDC, Cranfield University, Cranfield, UK, 3–4 June 2014.

                Address for correspondence: Dr. L. Daniel Maxim, Everest Consulting Associates15 North Main St., Cranbury, NJ 08512USA. E-mail: postsf@ 123456aol.com
                Article
                10.3109/08958378.2014.953276
                4245174
                25264933
                b2418a40-06d8-4901-945d-6abe49a7ad42
                © 2014 Informa Healthcare USA, Inc. All rights reserved: reproduction in whole or part not permitted

                This is an open-access article distributed under the terms of the CC-BY-NC-ND 3.0 License which permits users to download and share the article for non-commercial purposes, so long as the article is reproduced in the whole without changes, and provided the original source is credited.

                History
                : 25 June 2014
                : 31 July 2014
                : 5 August 2014
                Categories
                Review Article

                Toxicology
                biopersistence,epidemiology,fiber dimensions,mesothelioma,pleural plaques,refractory ceramic fiber,rock wool

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