Asbestiform antigorite from New Caledonia
Dr. Jasmine Rita Petriglieri
Department of Chemistry, University of Torino
Centro Scansetti «G. Scansetti» Interdepartmental Center for Studies on Asbestos and Other Toxic Particulates Universe of fibres ALL PARTICLES
ELONGATE OTHER Commercial/regulated definition PARTICLES (EMP) NOA are the six minerals that are currently identified as asbestos (were commercially INORGANIC ORGANIC exploited). minerals, mineraloids, and e.g., plant fibres and material made from minerals synthetic fibres
Mineralogical definition
Discriminate fibrous mineral from non- ASBESTIFORM MINERAL FIBRES NON ASBESTIFORM (EMPs from mass fibre, cross fibre and slip fibrous form (e.g., acicular, tabular, INORGANIC FIBRES fibre occurrences ) prismatic, …). Chemical alteration of mineral is considered.
REGULATED OTHER ROCK FORMING ASBESTOS MAN MADE Health-oriented definition MINERALS and erionite, fluoro-edenite, INORGANIC MINERALOIDS Identify any hazardous elongated mineral chrysotile, amosite, winchite, richterite, FIBRES (EMPs) particles (EMP) that requires to limit human crocidolite, glaucophane, anthophyllite-asbestos, antigorite, palygorskite, exposure. Most challenging. tremolite-asbestos, talc, minnesotaite, and actinolite-asbestos sepiolite
2 adapted from TAP (2018) 361, 185 Antigorite
MONOCLINIC OR ORTHORHOMBIC
Modulated wave-like 1:1 layer, with polarity inversion every half wavelength (Capitani and Mellini, 2004)
Chemical composition deviates from that of the other serpentine minerals, because of
discrete Mg(OH)2 loss
The variable modulation gives rise to a polysomatic series, with general formula:
M3m-3 T2mO5m(OH)4m-6 where m is the number of tetrahedra within a wavelength (Mellini et al., 1987; Otten, 1993) 3 May we define antigorite asbestiform?
Fibrous Antigorite from Rowland Flat area, Barossa Valley, South Australia (Keeling et al., 2008) 4 May we define antigorite toxic?
«Currently there is a limited number of in vitro and in vivo toxicological investigations performed on lamellar and fibrous antigorite and the results of the studies are not conclusive on antigorite toxicity.»
5
The New Caledonia
7 modified after Cluzel et al., 2001 Asbestos assessment in New Caledonia
1994 First evidence of environmental exposure to asbestos (Luce et al., 1994)
The government of NC launches a surveillance program to evaluate the 2005 potential professional exposure to asbestos.
Ban of the use of asbestos (Arrêté n° 2007-767/GNC) 2007 First geological survey of potentially NOA occurrences in ultrabasic units
Promulgation of the decree concerning the protection of workers against risks arising from 2010 asbestos exposure (Délibération n°82 du 25 août 2010)
Epidemiological correlation between mesothelioma and environmental exposure to 2011 fibrous serpentine minerals (Baumann et al., 2011)
Introduction of a protocol for best practises in mining sites to prevent and manage 2015 asbestos pollution (Guide des bonnes pratiques minières) 8 Environmental exposure to NOA
DOMESTIC EXPOSURE Melanesian houses are covered with raw earth and tremolite-Pö whitewash.
Quenel, Cochet (2001)
Baumann (2010) 9 Environmental exposure to NOA
ENVIRONMENTAL EXPOSURE
Lahondère (2007) «Malignant Mesothelioma (MM) in New Caledonia is associated with the presence of fibrous serpentine»
10 Hiengène, Tendo tribe from Lahondère, 2007 Mapping of NOA occurrences DIMENC/SGNC-BRGM
12 Occupational exposure to NOA
Ni-ore exploitation from lateritic deposits
3 mining industry Koniambo-KNS 23 open mines
Tontouta mine
Doniambo-SLN Goro-VALE NC
13 NOA occurrences in lateritic units
14 modified after Lahondère, 2012 Under humid sub-tropical conditions, natural deposits of asbestos shall be subjected to a stronger pedogenic alteration
Mont Dore, NC NOA occurrences in lateritic units
P Antigorite Tremolite E D O G E N I C
A L T E R A T I O N 16 Sevin et al., 2014 The asbestos regulation in New Caledonia
Antigorite in the list of the regulated-asbestos
No discrimination between antigorite and fibrous/asbestiform antigorite
No analytical method for the identification and quantification of fibres
No indication about environmental exposure was provided
17 Mining companies risk-management
defines how to measure the likelihood of exposure RISK EXPOSURE Exposure x Hazard
HAZARD
defines what makes a mineral fibre hazardous
Guide des bonnes pratiques minières en matière de gestion du risque amiante environnemental, 2015 18 Mining companies risk-management
19 Guide des bonnes pratiques minières en matière de gestion du risque amiante environnemental, 2015 General strategy for risk evaluation in a natural site
in the frame of the HAZARD evaluation, we need to define the properties of a fibrous mineral that have an impact on human health the metrics (aspect ratio, crystallochemistry, persistence, …)
in the frame of EXPOSURE assessment, we need to define standard methods and classifications → Geological NOA-risk model
20 Macroscopic features of Caledonian antigorite
An evident lack of cohesion and a very altered appearance characterized the NC rock-fragments.
Most of antigorite displays a silky FIBRO-LAMELLAR SHAPE
21 Petriglieri et al. - accepted Optical investigation: textural appearance
Star- and fan- shaped blades Interpenetrating texture
Antigorite samples show a greater types of shapes and intergrowths
lath-shaped lamella fibrous-lamellar blade Even the same sample can display the co-existence of several different textures
22 Petriglieri et al. - accepted SEM images: morphological aspect
FIBRO-LAMELLAR
ANTIGORITE Antigorite has the form of fibro-lamellar crystals with regular or irregular endings
Lamellar antigorite gradually cleaves in fibrous like particles, assuming a fibro-lamellar habit
23 Petriglieri et al. - accepted SEM images: morphological aspect
low-altered high-altered
bundles of fibrous particles with splaying ends lamellar-bladed elongated particles 24 Intergrowth of serpentine phases
Antigorite
25 Petriglieri et al., 2019 Intergrowth of serpentine phases
Raman peaks in OH-stretching region confirm the intergrowth of fibro-lamellae of antigorite and compact bundle fibres of chrysotile
Petriglieri et al., 2015; 2019 26 Finely intergrowth of antigorite and chrysotile
Chrysotile ?
27 Finely intergrowth of antigorite and chrysotile
59 spot analyses have been acquired, pointing the laser beam on various fibro- lamellar particles and contact areas with Atg each other
All OH stretching peaks generally attributed to antigorite and chrysotile co-exist together in a complex “doublet”
28 Finely intergrowth of antigorite and chrysotile
TEM confirmed the double nature of this sample, which consists of the intimate intergrowth of fibrous antigorite and chrysotile fibres Antigorite at the micro-scale
Chrysotile 29 Which properties make asbestos hazardous?
PATHOGENIC PROPERTIES OF ASBESTOS
Fibrous habit asbestos fibres penetrate deeply into the lung. Long (> 5 m), thin (< 3 m) and high-aspect ratio (length/diameter 3) are pathogenic; a long and thin fibre is more dangerous than a short and thick one (Stanton’s hypothesis, 1981). macrophage recruitment High biopersistence clearance once in the lung, asbestos fibres are not dissolved and frustrated phagocytosis may stay within the lung for decades. They are not inhaled macrophage efficiently cleared out by macrophages, elicit fibre activation inflammation and may eventually translocate to other inflammatory factors organs. death of macrophage
Surface reactivity Membranes asbestos fibre surface is chemically reactive and can damage biological media or living cell, altering cellular
basal metabolism. Particle and cell derived Enzymes ROS (reactive oxygen species)
DNA
30 Old and new approaches (e.g., Gualtieri, Mossmann, Roggli, EMU Notes, 2018 - https://doi.org/10.1180/EMU-notes.18) Evaluation of potential toxicity of fibrous antigorite
P E EXPERIMENTAL DESIGN D O Physico-minero-chemical G characteristics E N Cell-free chemical reactivity I Cellular toxicity C
A L T SAMPLES E 3 fibrous Atg (NC) R A non-fibrous Atg T I negative CTRL (MMVF) O N positive CTRL (UICC Ctl)
31 Comparing differently altered antigorite samples non-fibrous Atg low-altered
WHO (1997) COUNTING CRITERIA
Length > 5 μm Diameter < 3 μm Aspect ratio ≥ 3:1 mid-altered high-altered
Amount of respirable fibres is similar (30-40%) for all the alteration status
32 First results on antigorite toxicity
low-altered mid-altered high-altered non-fibrous chrysotile MMVF
MH-S A549 MH-S A549 MH-S A549 MH-S A549 MH-S A549 MH-S A549 Cytotoxicity - - * ** ** ** - - ** ** - - ROS generation - - - ** * - - - ** * - - GSH stress depletion - - ** ** ** ** - - ** ** - - PPP inactivation ------** ** - -
Oxidative HO-1 induction - - - * - - - - ** ** - - NO production - - ** ** ** ** - - ** ** - -
TNF-α
production - - - - ** - - - ** - - - Inflammation DNA nd nd nd nd nd nd damage - * * - ** - Lipid
damage peroxidation - - - * - * - - * * - - 33 Biomolecule First results on antigorite toxicity
low-altered mid-altered high-altered non-fibrous chrysotile MMVF
MH-S A549 MH-S A549 MH-S A549 MH-S A549 MH-S A549 MH-S A549 Cytotoxicity - - * ** ** ** - - ** ** - - ROS generation - - - ** * - - - ** * - - GSH stress depletion - - ** ** ** ** - - ** ** - - PPP inactivation ------** ** - -
Oxidative HO-1 induction - - - * - - - - ** ** - - NO production - - ** ** ** ** - - ** ** - -
TNF-α
production - - - - ** - - - ** - - - Inflammation DNA nd nd nd nd nd nd damage - * * - ** - Lipid
damage peroxidation - - - * - * - - * * - - 34 Biomolecule Comparing with chrysotile pathogenicity
LDH (cell death) Cytotoxicity increases with alteration of antigorite. Altered antigorite samples are less cytotoxic than Ctl chrysotile ** high-altered **
* * mid-altered * Cytotoxicity relies non-fibrous Atg on fibre surface low-altered MMVF chemistry
35 General strategy for risk evaluation in a natural site
in the frame of the HAZARD evaluation, we need to define the properties of a fibrous mineral that have an impact on human health the metrics (aspect ratio, crystallochemistry, persistence, …)
in the frame of EXPOSURE assessment, we need to define standard methods and classifications → Geological NOA-risk model
36 Geological NOA-risk management
Robust asbestos-oriented geological model
Reliable sampling strategy
NOA quantification
NOA-risk identification
37 Field survey on Tontouta mining front
Cr mine
Ni-ore
38 Geology and petrography of Ni-ore site
Red-limonite with Mn-oxides. Image Serpentinized harzburgite (saprolite) removed
Sector 13 _ Ni content: 1.92 wt% Image removed
(fibrous) antigorite Harzburgite (dunite?) 39 Geology and petrography of Ni-ore site
Red-limonite with Mn-oxides. Image Serpentinized harzburgite (saprolite) removed
Sector 13 _ Ni content: 1.92 wt% Image removed
(fibrous) antigorite Harzburgite (dunite?) 40 Take home messages
Unaltered non-fibrous antigorite is not active in any toxicological assay investigated.
Caledonian antigorite exhibits a fibro-lamellar habit, resulting in a greater variability in texture and morphology.
Pedogenic alteration of NOA affects the potency to disperse fibers into the environment.
Altered fibrous antigorite shares with chrysotile key physico-chemical features and toxic effects in vitro.
NOA alteration modifies the cell toxicity of antigorite suggesting a role of surface chemistry in the potential pathogenicity of fibrous antigorite. Thanks to all partners
Supporter and funder of UniTO – “G.Scansetti” Center ISEA Laboratory - UNC UniPR the «Amiante et Bonnes Francesco Turci Christine Laporte-Magoni Emma Salvioli Mariani Pratiques» project Maura Tomatis Monika Le Mestre Danilo Bersani Elena Gazzano Nahza Salmaoui-Folcher Mario Tribaudino Chiara Avataneo Peggy Gunkel-Grillon Elisabetta Aldieri Roberto Cossio Roberto Compagnoni Société Minière Montagnat Bice Fubini CNR-IGG UniMIB Fabrizio Piana Alessandro Cavallo Luca Barale Thank you!