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Article

Asbestos Bodies in Human Lung: Localization of Iron and Carbon in the Coating

by
Alessandro Croce
1,2,*,
Giorgio Gatti
3,
Antonio Calisi
2,
Laura Cagna
2,
Donata Bellis
4,
Marinella Bertolotti
1,
Caterina Rinaudo
2 and
Antonio Maconi
5
1
SSD Research Laboratories, Research Training Innovation Infrastructure, Research and Innovation Department (DAIRI), Azienda Ospedaliero-Universitaria SS. Antonio e Biagio e Cesare Arrigo, Via Venezia 16, 15121 Alessandria, Italy
2
Department of Science and Technological Innovation, University of Eastern Piedmont, Viale T. Michel 11, 15121 Alessandria, Italy
3
Department for Sustainable Development and Ecological Transition, Piazza S. Eusebio 5, 13100 Vercelli, Italy
4
Centre “G. Scansetti” Via Pietro Giuria 9, 10100 Turin, Italy
5
Research Training Innovation Infrastructure, Research and Innovation Department (DAIRI), Azienda Ospedaliero-Universitaria SS. Antonio e Biagio e Cesare Arrigo, Via Venezia 16, 15121 Alessandria, Italy
*
Author to whom correspondence should be addressed.
Geosciences 2024, 14(3), 58; https://doi.org/10.3390/geosciences14030058
Submission received: 30 October 2023 / Revised: 7 February 2024 / Accepted: 16 February 2024 / Published: 23 February 2024
(This article belongs to the Section Natural Hazards)
Browse Figures
Versions Notes

Abstract

:
Asbestos is a term that includes six fibrous mineral phases related to different lung diseases, including asbestosis, lung cancer, and Malignant Pleural Mesothelioma (MPM). Since the last century, these minerals have been widely studied under their mineralogical/chemical and physical aspects with in vivo and in vitro studies to understand the mechanisms of their carcinogenicity. There are several techniques described in the literature, as optical and electron microscopies, for the identification of coated (asbestos bodies, ABs) and uncoated fibers, but only micro-Raman spectroscopy permits a sure characterization of these minerals—and of the related phases—directly in the histological sections of pulmonary parenchyma without any manipulation. In this case, the risk of the loss of associated inorganic phases from asbestos bodies (ABs) and fibers (e.g.: iron or carbonaceous micro-particles) is avoided. Asbestos bodies are produced by the activity of alveolar macrophages with degradation/inactivation of asbestos fibers. Inside the alveolar macrophages, organic and inorganic material settles on the foreign fibers forming an iron-rich proteic and carbonaceous coating. In this study, Variable Pressure Scanning Electron Microscopy with annexed Electron Dispersive Spectroscopy (VP-SEM/EDS) and micro-Raman spectroscopy were applied to the characterization of the phases in the ABs. Characterization of carbonaceous materials (CMs), observed in pristine asbestos phases in previous works, was therefore performed, addressing the micro-Raman laser beam on different points of the asbestos bodies, and Raman mappings on ABs were carried out for the first time. Coupling the data obtained by VP-SEM/EDS and micro-Raman spectroscopy, it was possible to collect information about the iron and carbonaceous phases adhered to the fibers, probably lost during the classical tissue digestion procedures. Information about both mineral and carbonaceous components might be useful to understand the whole structure of “asbestos bodies” and the inflammogenic and carcinogenic effects of the asbestos phases coupled to CMs, that might derive from cigarette smoke or from environmental pollution; this study might be useful to deepen also the possible detrimental role of ABs in the tissues.

1. Introduction

The term “asbestos” indicates six natural mineral fibers that are well known for their mechanical/chemical properties (e.g.: resistance to heat, corrosion, and electricity) and for their carcinogenic effect on human health [1,2]. These minerals are: (i) tremolite (Ca2Mg5[Si8O22](OH)2), (ii) actinolite (Ca2(Mg,Fe2+)5[Si8O22](OH)2), (iii) anthophyllite ((Mg,Fe2+)7[Si8O22](OH)2), (iv) cummingtonite-grunerite (amosite) ((Fe2+,Mg)7[Si8O22](OH)2), (v) riebeckite (crocidolite) (Na2Fe2+3Fe3+2[Si8O22](OH)2), and (vi) chrysotile (Mg3Si2O5(OH)4). Among them, the first five are amphiboles (double-chain silicates), and the last one is a phyllosilicate belonging to the serpentine family [3,4,5].
These minerals have been extensively extracted and used in factories, in particular during the industrial expansion in the XX century: of the six phases, the most manufactured were chrysotile, crocidolite, and amosite asbestos. On the other hand, since the beginning of the last century, different researchers have highlighted more and more the evidence relating asbestos exposure to respiratory diseases—i.e., lung carcinoma, asbestosis, Malignant Pleural Mesothelioma (MPM) [6,7]—and also to tumors affecting other sites (e.g.: gastrointestinal or reproductive system) [1,8,9,10,11,12,13,14,15]. For this reason, these minerals have been studied not only under their mineralogical aspects but also with the goal to understand the carcinogenetic properties and the fibrogenetic activities [16,17,18,19,20,21,22,23,24,25,26,27,28,29,30,31]. Many research studies have been addressed to define their structures, chemical compositions, and physical properties but often considering the raw bulk samples [5,24,27,31]. In the past and in recent years, more performing methodologies have been developed allowing a deeper characterization of the raw materials, also inside the lungs and/or other biological materials without the need for any manipulation of the samples [32,33,34,35].
Moreover, in the last years, the research community focused attention on the key point that is still unclear: the relationships between the mineralogical inorganic components and the biological medium, in particular in the fiber/cell contact surfaces [36,37,38]. Nevertheless, also in these studies, the samples underwent different manipulation procedures that can affect the samples themselves. So, there is still the need to carry out additional analyses using a technique that does not require sample preparation.
One of the methodologies allowing this kind of analysis is micro-Raman spectroscopy. This technique, thanks to the microscope annexed to the spectrometer, allows the characterization of the fibers in different areas and the identification of phases on their surfaces [34,35].
Croce et al., 2015, 2018, demonstrated that micro-Raman spectroscopy allows to characterize different iron compounds—goethite (FeO(OH)), hematite (Fe2O3), and jarosite (KFe33+(SO4)2(OH)6)—on erionite fiber surfaces [39] and carbonaceous materials (CMs) lying on standard samples of the three most manufactured asbestos phases—crocidolite, amosite, and chrysotile [34,35]. The technique highlighted, in an unequivocally way, the position of these phases, with a great advantage with respect to the methodologies requiring sample preparation (e.g.: X-ray diffraction, gas chromatography, UV spectrophotometry, IR, mass spectroscopy, and Scanning and Transmission Electron Microscopies) [40,41,42,43,44,45,46,47,48].
In this study, micro-Raman spectroscopy has been applied to the characterization of the phases composing asbestos bodies (ABs, coated asbestos fibers) [32] inside pulmonary histological sections of patients affected by MPM. ABs derive from the frustrated phagocytosis carried out by lung macrophages, which produce a deposition of minerals and iron proteins on fiber surfaces; this is due to fiber dimensional parameters (length ≥ 5 μm, thickness ≤ 3 μm, and length/thickness ratio > 3) [11] that do not permit the fiber removal by the cells. These morphologies are typical markers of past asbestos exposures, and they represent a last attempt of the human body to isolate the fibers, but that might produce damage to the body itself. ABs are formed by an internal asbestos fiber (called “core”) and by a coating composed of iron-rich protein, mainly composed of ferritin containing the mineral ferrihydrite, acid mucopolysaccarides, phospholipids, and lung surfactant proteins (called “coating”) [36].
Rinaudo et al., 2010, demonstrated that micro-Raman spectroscopy is able to identify a crystallization of hematite from the iron-rich cores of the protein coating, under the power of the 632.8 nm laser [49], considering the 1200–200 cm−1 spectral range. The results obtained on asbestos bodies of different shapes will be presented, considering also the spectral range where organic fingerprints [34,35] lie, trying to understand if carbonaceous materials may be identified also in these biological materials. In this work, the goal will be the identification of other organic components, considering, in particular, the 1800–1200 cm−1 spectral range, where the CM first-order bands lie, trying to understand if carbonaceous components are identifiable after AB formation.
In fact, during tissue digestion or sample preparation, it is possible to lose some organic or inorganic components of ABs, and the application of micro-Raman spectroscopy may be useful to observe and integrate the data obtained with other techniques. Moreover, it is possible to obtain Raman maps, visualizing where the different components are present, and a second goal of this work is to apply this methodology for the first time to understand also where the different phases in the ABs are localized.
Coupling the data obtained by applying this technique and SEM/EDS analyses may be useful for understanding the features from the chemical and spectroscopical points of view. In fact, the application of SEM/EDS directly on histological sections is useful to chemically identify the mineral fibers, also when they are covered by the iron-rich proteins: in this work, the method presented in Croce et al., 2013 [32], has been applied, with the aim of better understanding which iron is ascribable to the inorganic fiber.
The obtained data, both from the mineral phase and from the adhered particles on the iron-protein covering, might be useful for future studies in the field of asbestos-related diseases.
In fact, the first problem in asbestos fiber identification is the understanding of the mineral phase inside the covering, and future application—and improvement—of these non-destructive techniques might be useful in medical legal debates.
Secondly, the characterization and the localization of other phases located next to asbestos fibers or ABs might be useful to studies concerning the carcinogenic effects of the different particles. For example, keeping in mind that cigarette smoke has a synergistic effect with asbestos oncogenic consequences [36], in the future, a study analyzing a greater number of patients (or on in vivo or in vitro samples) might be useful to improve the knowledge of the mechanisms about the disease development.
So, the strict collaboration of geologists, geoscientists, and mineralogists, considered in this case as “medical geologists”, with other experts in different disciplines (e.g.: health sciences, pathology, epidemiology) might be useful to reach the goal aimed at eradicating or reducing the effects of the diseases and understanding the pathways to find long-term solutions [50].

2. Materials and Methods

Lung samples from one patient affected by MPM, diagnosed postmortem, were embedded in a paraffin block and then cut using a microtome into 5 µm thick sections. The patient’s information was opportunely anonymized to the analysts. Because this study is an exploratory analysis and all the data were anonymized, no informed consent was obtained from the patient, and it was not necessary in accordance with our Ethical Committee, so the collection and inclusion in the analysis of the patient’s information on exposure and life history were not carried out. The sections were fixed on plastic slides in order to avoid interference between the chemicals composing the glass and the ones forming the fibrous materials contained inside the ABs. The slides were put in an oven at 60 °C overnight to degrade the paraffin film embedding the tissues. The sections were then observed under an Optical Microscope (OM), equipped with two polarizers, to identify the ABs, and their positions were defined by means of an x-y grid for further analyses, both by SEM/EDS and micro-Raman spectroscopy.
SEM/EDS analyses were performed using an ESEM Quanta 200 SEM (FEI Company, Hillsboro, OR, USA), equipped with an EDS (EDAX, Mahwah, NJ, USA). Back-scattered images (BSE), characterized by white/black contrasts produced by inorganic phases embedded inside the tissues, allowed easy identification of the silicate fibers [11,32]. The experimental conditions were: pressure = 90 Pa, working distance = 10 mm, and accelerating voltage = 20 kV. EDS spectra were collected and processed using GENESIS software, v. 3.6. To determine the elemental composition of the observed inorganic phases, EDS microanalyses were carried out following the procedure described in our previous works [11].
Raman analyses were carried out using a JobinYvon HR Evolution micro-Raman spectrometer (HORIBA JobinYvon, Paris, France), equipped with a 532 nm Nd:YAG laser source. Autocalibration of the spectroscope was performed fixing the ~520.6 cm−1 band of the Si reference sample before every experiment. The spectra were collected addressing 3.2% of the full laser power directly on the fiber embedded in the tissue; the spectra were acquired with 1 exposure of 100 s for each spectral range, under the 80x objective of the microscope coupled to the instrument. Employing this experimental set-up, well-resoluted spectra and maps could be collected. Raman maps were recorded using the same parameters and rectangular areas, chosen on the basis of the AB morphologies, were analyzed in order to obtain images characterized by two-dimensional high resolutions.
Moreover, a fitting procedure has been applied to representative spectra, using the software Fytik v. 0.9.8, to define the order degree of the organic component adhered to the asbestos body. It was carried out considering six different components, one Gaussian and five Lorentzian, using a dedicated script described in Croce et al., 2021 [51]. The bands are called D1 (lying at about 1330 cm−1, deriving from defective carbons), G (about 1550–1580 cm−1, related to the extension of ordered regions), D2 (related to the D1 band, lying at about 1600–1615 cm−1), D3 (the Gaussian one, at 1450–1550 cm−1), D4 (1150–1230 cm−1), and D5 (1060–1120 cm−1). This process is necessary to obtain the best fit to calculate shapes and intensities of the bands in the 800–1800 cm−1 range: in particular, the intensities of the D1 and G bands are important to calculate the R1 ratio, related to the disorder degree of the carbonaceous materials.

3. Results

Histological sections from an MPM patient were carefully studied under an OM to detect the presence of ABs and localize them in the tissues. As shown in Figure 1, they can be classified on the basis of their shape, color, and morphology. The observed ABs appeared dark or red/brown (Figure 1a,b), often surrounded by great areas of black aggregates (Figure 1c).
A set of histological sections from the lung tissue of the same patient were cut and placed on plastic slides in order to carry out SEM/EDS analysis to identify the inorganic phase inside the AB, following the same methodology described in the work of Croce et al., 2013 [32]. Figure 2 shows an example of a well-developed AB: its length is about 31 μm, whereas the fiber diameter (measured on an area less covered by iron proteins) is about 400 nm, and the protein covering shell showed a diameter ranging from ~2 to ~2.5 μm.
Thanks to the dimensions of the asbestos body in Figure 2, different punctual EDS analyses along lines (about 30 total lines) have been performed, and the chemicals composing the fiber could be evaluated. With respect to the study of Croce et al., 2013 [32], here the analyses were acquired both along and perpendicular to the elongation axis of the fiber, to obtain a more precise determination of the chemical elements constituting the inorganic fiber and the iron proteins. It must be considered that, in applying the described procedure, an unequivocal attribution of iron to the fiber or to the covering results is very difficult. Nevertheless, it was demonstrated that phosphorus is a component proper of the ferritin core of the proteins covering the inorganic fiber, so the identification of this chemical element might be used as a discriminating factor between the inorganic and the organic iron components, due to the fact that phosphorus is not an element composing the asbestos fibers [36,38,52]. So, it can be assumed that iron is ascribable to the inorganic fiber when P is not detected, although the obtained values are only semi-quantitative.
An example of the positions of the different analyzed points along and perpendicular to the asbestos body is shown in Figure 3, and the respective semi-quantitative obtained values are reported in Table 1.
The data reported in Table 1 show that P is not detected in the points less covered by the iron proteins. On the other hand, it has been demonstrated that this chemical element is present in the structure of the iron-protein covering, which is characterized by a structure similar to that of ferrihydrite [36,38,52]. Considering this aspect, it can be assumed that almost all the Fe detected in points #1 and #2 of line 1 in Table 1 can be ascribed to the mineral fiber. In the other analyzed points, it is impossible to attribute the iron to the inorganic or the organic phases [53,54,55].
In Figure 4, a schematic representation of some selected analyses acquired in the red line points in Figure 3 is reported (the numerical atoms % values are reported in line 1 in Table 1). The P peak appears less intense (or it is not detected at all) in the spectra recorded in the less covered parts of the asbestos body (spectra #1 and #2), allowing to ascribe the iron to the inorganic fiber.
The different elements ascribed to inorganic components or to the biological medium, i.e., P and Ca, can be localized, but it was impossible to detect variations regarding carbon, which was always the main component in each analysis (>85% in every point, not reported in Table 1). Moreover, the SEM/EDS technique allows to qualitatively characterize the inorganic fiber inside the iron-protein coating, superimposing the spectra as described in the work of Croce et al., 2013 [32]. In fact, considering the P detected in the different analyzed points, the chemical elements ascribable to the fiber may be identified (Figure 5). In this case, the superimposed spectra are three: the spectrum obtained analyzing a point where only the iron-protein coating is present (analysis #3 in line 2, grey in Figure 5), a second one recorded on a less covered area of the fiber (analysis #1 in line 1, black in Figure 5), and a third one where the two components (protein and fiber, analysis #10 in line 1, orange in Figure 5) were recognizable.
As can be seen in Figure 5, iron is a component proper of the fiber (black line in Figure 5), with these peaks appearing with lower intensity with respect to the ones observed when the protein component (grey and orange in Figure 5) is present. Iron peaks show higher intensity in spectra recorded where fiber and protein components are present (analysis #10 of line 1 in Figure 5). Considering the data recorded on this asbestos body, the inorganic fiber is composed of Si > Mg > Fe in decreasing amounts, so it may be ascribed to the asbestos phase “anthophyllite”.
In addition to OM and SEM analyses, ABs observed in the lung section of the same patient have been characterized under micro-Raman spectroscopy, in order to characterize not only the iron covering but also to evaluate the presence of carbonaceous phases, “unidentifiable” in the SEM/EDS analyses. The laser beam was addressed onto areas appearing most covered by iron proteins during OM and SEM observations.
In Figure 6, an example of AB, observed under the OM annexed to the Raman spectroscope (80X objective), is reported. In this case, subsequent acquisitions on the more covered portion of the fiber were carried out, considering the 1800–100 cm−1 spectral range. The applied method was the same as that described in the work of Rinaudo et al., 2010 [49], where only the spectral range of 1200–200 cm−1 was considered. So, recognition of both inorganic and organic phases may be carried out taking into account the spectral range considered in this work. The 1800–100 cm−1 range was chosen to obtain well-resoluted spectra and to define after how much time the band features were changing during acquisition, to understand if mapping analyses were able to give results preventing sample modifications.
Figure 6 shows spectral features evolution in the subsequent spectra. In the analyses carried out during the first ~30 min, the most prominent bands are related to carbonaceous material (CM) [34,35]. In the spectra recorded after this time, the bands related to the organic component decrease in intensity, and an increase in the intensities of the bands related to iron oxides is detected (see Discussion section for more details). Moreover, the bands related to these last phases show an evolution also in Raman shifts, up to a feature ascribable to the iron oxide “hematite”, Fe2O3, and the disappearing of signals related to carbon phases can be observed: note that the band lying at about 1300 cm−1 is ascribed to the second order of the iron oxide phase when CMs are not detected.
As it concerns CM Raman bands, a fitting procedure was applied in the 1800–800 cm−1 spectral range, considering the six bands indicated in the Materials and Methods section; the results are reported in Figure 7. In the analyzed case, the intensities of the two Raman bands are 109.28 (a.u., D1 band) and 75.54 (a.u., G band), giving an R1 ratio of 1.45. This value indicates a disordered structure of the CMs on the asbestos body, with a ratio similar to the ones obtained from CMs observed on crocidolite fiber surfaces [34]. The values of intensities of D1 and G bands observed in the other ten representative spectra- and their relative R1 ratios—from CMs on ABs observed inside the same histological sample—are reported in Table 2.
As can be observed in Table 2, the R1 ratio shows a mean value of 1.44, with a maximum value of 1.49 and a minimum of 1.42, so the order degree of the analyzed CMs is comparable.
Starting from these results, it was possible to set up the instrument configuration and parameters in order to obtain spectra without modifying (morphologically and chemically) the analyzed ABs. Raman mappings were therefore carried out on different covered fibers. In Figure 8, a Raman mapping on a well-developed formation is reported.
Three Raman spectral ranges were considered for map generation: (i) ~550–700 cm−1, where the Si-O-Si symmetric stretching bands lie (in red in Figure 8) for the silicate component; (ii) ~1500–1650 cm−1, where the G and D2 bands of the CMs are observed (green in Figure 8); (iii) ~2700–3000 cm−1, to collect the map relative to the paraffin wax embedding the tissue (blue in Figure 8).
From the green map in Figure 8c, it is evident the presence of a carbonaceous covering, adhered to the iron protein capsule embedding the fiber. As it concerns the recognition of the silicatic component inside the asbestos body, it is difficult to assign the mineral phase to it. In fact, only in a very small portion of the corpuscle is it possible to observe very weak signals, which are more visible only after the superimposition of the three Raman maps (see Figure 8d).

4. Discussion

In this work, two complementary techniques—SEM/EDS and micro-Raman spectroscopy—were applied to the characterization of the components constituting the typical marker for asbestos exposure, the “asbestos bodies”. As specified before, SEM/EDS allows the collection of spectra relative to the chemical components constituting the different areas of the observed sample, whereas Raman spectroscopy allows to obtain information related to the chemical bonds of the analyzed materials. The development of a methodology that allows the identification of not only the inorganic components but also the relationships between biological and inorganic components, without removing the tissues, may be very important to understanding the mechanisms of fiber pathogenicity.
In fact, manipulation procedures for the extraction of the asbestos fibers or bodies are often necessary with the consequent risk of losing the biological material (e.g.: during tissue digestion or ashing), altering both the chemical composition and the structure of ABs [37]. So, in the field of medical geology, it is really important to develop a method allowing the characterization of ABs directly inside the tissues, to maintain unaltered these formations and their relationships with the organic matrices.
In this work, SEM/EDS and micro-Raman spectroscopy were applied to histological samples routinely analyzed by pathologists to better define the inorganic and the organic components compared to the past works [32,49]. In fact, compared to [32], iron has been deeply characterized, to define if it was possible to distinguish the inorganic component from the organic one. Moreover, compared to [49], also analyzed was the Raman range where the first-order bands of CMs lie, which were analyzed only in raw asbestos in previous works [34,35], to determine if also these phases were identifiable directly in histological sections.
As it concerns the SEM/EDS technique, in the operative conditions applied in this work, only qualitative data could be obtained: nevertheless, it was possible to distinguish the mineral phase by comparing the obtained data to the reference spectra previously collected on pure samples.
Considering the organic component, due to the value of detected carbon (a mean > 85%), it was not possible to extrapolate information about the presence of CMs or other organic components adhered to the asbestos fibers. Nevertheless, observing the data relative to the iron element, it could be related to the organic or the inorganic phases: in fact, when phosphorus was detected, it can be ascribed to the iron-protein covering, due to the strict relationship between these two chemical elements, whereas it is attributed to the silicatic phase when P was not detected. In fact, it has been demonstrated that phosphorous can be adsorbed on fiber surfaces during amphibole transformation in contact with tissues [38], and it is detected mainly inside the protein coating [36]. In the present work, it was possible to obtain the same result observed by Avramescu et al., 2023 [36], without the removal of the biological component.
It has been demonstrated that SEM/EDS is very useful for mineral recognition also when the fiber is embedded inside iron-protein coverings. Considering the distribution of phosphorus in the ABs, it is also possible to exclude the detected iron from the chemical composition of the mineral phase. Phosphorus presence in chemical composition might be useful to better identify the mineral phase associated with the fibrous morphologies, principally in a qualitative analysis, when the fiber is composed also of iron (e.g.: amosite-anthophyllite, actinolite-ferroactinolite, etc.). On the other hand, no information about the other organic components can be obtained.
Micro-Raman spectroscopy is another technique that allows the collection of data from ABs directly inside the biological medium, maintaining the relationships between the inorganic and the organic components. When the laser beam gives too much energy, the iron contained inside the protein cores tends to reorganize its structure until the formation of the mineral hematite—chemical formula Fe2O3. Its formation is related to the degradation of CM particles adhered to the covering surface: in fact, collecting subsequent spectra on the same point of the asbestos body, it was possible to observe the disappearing of the D and G bands ascribed to the carbonaceous component in relation to the increasing intensity of the Raman bands ascribed to the iron oxide phase.
This tendency is more frequent in asbestos bodies more covered by carbonaceous material: from the optical point of view, the covering level is associable with a darker color (i.e.: dark red or brown) of the morphology.
Applying a fitting procedure to evaluate the numerical parameters of the different bands lying in the range of 800–1800 cm−1, it is possible to determine the order degree of the observed carbonaceous materials. In future studies, it might be interesting to evaluate the order degree of these particles in different patients, to determine if the Raman spectra of the organic material can be useful to obtain information about the organic components on the fiber surfaces after interaction with lung tissues.
For example, Avramescu et al., 2023 [36], observed that iron-protein covering was denser in smokers, whereas there were different concentric rings in non-smokers, suggesting a more variable iron supply in AB formation. This study was carried out using SEM, focused ion beam (FIB), and transmission electron microscopy (TEM) after digestion of the tissues. A future application of micro-Raman spectroscopy to a set of samples deriving from smokers and non-smokers might improve the understanding of these structures from another point of view, with the advantage that the analyses can be performed directly inside the tissues, preventing the loss of information about the particles adhered to AB surfaces.
It must be considered that carbon black is listed as a group 2B carcinogen by the IARC [57], and it is related to an increase in lung cancer risk [58,59,60], so detection and localization of CMs related to asbestos fibers may be useful for future studies concerning the comprehension of cancer development in terms of synergistic effects.
Moreover, micro-Raman spectroscopy demonstrated its advantages also in mapping analyses, allowing the operator to understand where the different organic or inorganic phases are localized in the asbestos bodies. No well-developed Raman spectra of the mineral phase contained in the embedding were recorded: it may be due to the iron coating signal or to the loss of mineral structure undergone by the fiber. This point must be deepened in future studies.
In conclusion, the coupling of SEM/EDS and micro-Raman spectroscopy allows us to obtain information about the mineral phases contained inside the asbestos bodies and the other pollutants next to them, as carbonaceous materials, thanks to the direct analysis in the tissues, without particular manipulations. In the future, it might be interesting to apply these non-destructive techniques to a greater number of cases (or to samples with known exposures, as it is carried out in in vitro and in vivo studies), trying to provide some results that are useful to better understand what happens to the different inhaled (or also ingested) particles and fibers when they come in contact with the tissues. Moreover, it may be interesting to apply these techniques to different cohorts of patients exposed to different inorganic and organic pollutants, or to smoking and non-smoking patients, to observe whether differences in AB structures are identifiable.
In this way, the collaboration of the mineralogist with researchers of other biological and medical fields might improve the knowledge of the different respiratory and extra-respiratory diseases, considering them from the point of view of interdisciplinary studies in medical geology.

Author Contributions

Conceptualization, A.C. (Alessandro Croce); methodology, A.C. (Alessandro Croce); software, A.C. (Alessandro Croce); validation, C.R. and A.C. (Alessandro Croce); formal analysis, A.C. (Alessandro Croce); investigation, A.C. (Alessandro Croce); resources, C.R.; data curation, A.C. (Alessandro Croce); writing—original draft preparation, A.C. (Alessandro Croce), D.B., A.C. (Antonio Calisi), G.G. and C.R.; writing—review and editing, C.R., D.B. and A.C. (Alessandro Croce); visualization, A.C. (Alessandro Croce) and L.C.; supervision, C.R., M.B. and A.M.; project administration, A.C. (Alessandro Croce); funding acquisition, C.R. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

The study was conducted according to the guidelines of the Declaration of Helsinki, and approved by the Ethics Committees of the University of Torino (Turin, Italy) and of the Martini hospital (Turin, Italy) Ethical Committee of ASL TO2 (no. 38851 (protocol code 38851 on 29 July 2013).

Data Availability Statement

Data is contained within the article.

Acknowledgments

This work was supported by UPO (“Integrated system for the fibre pollution assessment in air and characterization of the fibrous phases in different matrixes”). The authors wish to thank the Editors and the anonymous referees for their work.

Conflicts of Interest

The authors declare no conflicts of interest.

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Figure 1. (a,b) Example of asbestos bodies observed in the patient’s lung tissue and showing a dark color (magnification 40× in (a) and 63× in (b)); (c) Black aggregates near the ABs (arrows indicate some short fibers); magnification 63×.
Figure 1. (a,b) Example of asbestos bodies observed in the patient’s lung tissue and showing a dark color (magnification 40× in (a) and 63× in (b)); (c) Black aggregates near the ABs (arrows indicate some short fibers); magnification 63×.
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Figure 2. (a) Low magnification of the lung tissue; inside the circle, the position of the asbestos body is highlighted. (b) Asbestos body of (a) observed at higher magnification. (c) Magnification of the left end of the AB.
Figure 2. (a) Low magnification of the lung tissue; inside the circle, the position of the asbestos body is highlighted. (b) Asbestos body of (a) observed at higher magnification. (c) Magnification of the left end of the AB.
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Figure 3. Schematization of the lines considered for the different chemical analyses, corresponding to the visible contained fiber (red points, named “line 1” in Table 1), the iron-protein covering (green points, named “line 2” in Table 1), and the data collected along a line perpendicular to the elongation axis of the fiber (yellow points, indicated as “line 3” in Table 1).
Figure 3. Schematization of the lines considered for the different chemical analyses, corresponding to the visible contained fiber (red points, named “line 1” in Table 1), the iron-protein covering (green points, named “line 2” in Table 1), and the data collected along a line perpendicular to the elongation axis of the fiber (yellow points, indicated as “line 3” in Table 1).
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Figure 4. EDS spectra acquired in the points considered along the fiber. The peak relative to C is not indicated.
Figure 4. EDS spectra acquired in the points considered along the fiber. The peak relative to C is not indicated.
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Figure 5. EDS superimposition of three spectra obtained on the iron-protein covering (grey), the less covered portion of the fiber (black), and the area where the fiber is more embedded by the organic component (orange).
Figure 5. EDS superimposition of three spectra obtained on the iron-protein covering (grey), the less covered portion of the fiber (black), and the area where the fiber is more embedded by the organic component (orange).
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Figure 6. Example of subsequent (“a” is the first analysis, “u” the last one) Raman analysis carried out on the asbestos body reported on the right. Shown is the asbestos body before and after the cycle of analysis.
Figure 6. Example of subsequent (“a” is the first analysis, “u” the last one) Raman analysis carried out on the asbestos body reported on the right. Shown is the asbestos body before and after the cycle of analysis.
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Figure 7. Fitting on a Raman spectrum obtained by analyzing the AB covering. The various colors indicate the different bands: G in blue, D1 in red, D2 in green, D3 in dark gray, D4 in pink, and D5 in light gray. The bands indicated by * are ascribed to the paraffin embedding in the lung tissue [56].
Figure 7. Fitting on a Raman spectrum obtained by analyzing the AB covering. The various colors indicate the different bands: G in blue, D1 in red, D2 in green, D3 in dark gray, D4 in pink, and D5 in light gray. The bands indicated by * are ascribed to the paraffin embedding in the lung tissue [56].
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Figure 8. (a) Asbestos body in lung observed by OM; the red rectangle indicates the area analyzed during Raman mapping. (b) Positions of the bands considered for Raman mapping (red = bands related to silicate phase; green = CMs; blue = tissue + paraffin). (c) Mapping of the bands reported in (b); (d) Superimposition of the mapping on the OM photograph.
Figure 8. (a) Asbestos body in lung observed by OM; the red rectangle indicates the area analyzed during Raman mapping. (b) Positions of the bands considered for Raman mapping (red = bands related to silicate phase; green = CMs; blue = tissue + paraffin). (c) Mapping of the bands reported in (b); (d) Superimposition of the mapping on the OM photograph.
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Table 1. Qualitative atoms % values obtained on the different points indicated in Figure 3.
Table 1. Qualitative atoms % values obtained on the different points indicated in Figure 3.
Atoms %P/Fe Ratio
SiMgFeNaCaSP
Line 1
#10.310.100.210.020.010.010.000.00
#20.340.120.250.000.000.000.000.00
#30.310.150.440.000.000.000.000.00
#40.270.090.650.060.050.030.070.11
#50.270.120.590.060.030.020.070.10
#60.290.120.470.060.030.030.060.13
#70.290.120.500.060.030.020.070.10
#80.290.120.500.060.030.030.060.12
#90.270.090.470.070.040.040.060.13
#100.280.130.530.090.040.040.080.15
#110.260.100.630.060.040.030.090.14
#120.250.110.710.030.040.040.040.13
#130.220.100.700.040.040.030.080.11
#140.200.120.740.080.050.030.110.15
#150.200.100.660.070.030.020.090.14
#160.210.080.480.070.030.020.040.08
#170.260.110.250.040.020.010.030.12
#180.250.110.290.060.020.020.040.14
Line 2
#10.040.050.310.030.050.010.050.16
#20.040.060.550.050.040.040.100.18
#30.020.080.780.070.060.030.100.13
#40.040.060.590.070.050.050.100.17
#50.060.050.210.070.040.040.040.19
#60.050.040.240.020.020.030.050.21
#70.060.100.740.070.050.040.130.18
#80.060.060.860.050.050.030.130.15
#90.050.040.830.070.050.040.130.16
#100.040.040.500.060.040.030.090.18
Line 3
#10.030.050.340.070.030.030.070.21
#20.060.050.520.070.030.030.090.17
#30.200.110.600.050.040.030.060.10
#40.060.050.680.060.050.030.100.15
#50.060.050.680.050.050.050.110.16
#60.040.040.690.030.040.030.100.15
#70.040.050.620.080.060.040.090.15
Table 2. Observed intensities of D1 and G bands in ten representative spectra and their calculated R1 ratios.
Table 2. Observed intensities of D1 and G bands in ten representative spectra and their calculated R1 ratios.
D1 Band IntensityG Band IntensityR1 Ratio
Spectrum #1272.12188.971.44
Spectrum #2154.78108.241.43
Spectrum #3150.93101.291.49
Spectrum #4159.03109.681.45
Spectrum #5177.60121.641.46
Spectrum #6169.23116.711.45
Spectrum #7154.56108.841.42
Spectrum #8148.96104.901.42
Spectrum #9143.5799.701.44
Spectrum #10145.9799.981.46
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Croce, A.; Gatti, G.; Calisi, A.; Cagna, L.; Bellis, D.; Bertolotti, M.; Rinaudo, C.; Maconi, A. Asbestos Bodies in Human Lung: Localization of Iron and Carbon in the Coating. Geosciences 2024, 14, 58. https://doi.org/10.3390/geosciences14030058

AMA Style

Croce A, Gatti G, Calisi A, Cagna L, Bellis D, Bertolotti M, Rinaudo C, Maconi A. Asbestos Bodies in Human Lung: Localization of Iron and Carbon in the Coating. Geosciences. 2024; 14(3):58. https://doi.org/10.3390/geosciences14030058

Chicago/Turabian Style

Croce, Alessandro, Giorgio Gatti, Antonio Calisi, Laura Cagna, Donata Bellis, Marinella Bertolotti, Caterina Rinaudo, and Antonio Maconi. 2024. "Asbestos Bodies in Human Lung: Localization of Iron and Carbon in the Coating" Geosciences 14, no. 3: 58. https://doi.org/10.3390/geosciences14030058

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