| Literature DB >> 32476920 |
Mickael Catinon1,2,3, Catherine Cavalin2,4,5, Cécile Chemarin1,3, Stéphane Rio1, Elisabeth Roux1, Mathieu Pecquet1, Anne-Sophie Blanchet1, Sylvie Vuillermoz1, Christophe Pison6, François Arbib6, Vincent Bonneterre7, Dominique Valeyre8, Olivia Freynet8, Jean-François Mornex9,10, Yves Pacheco11, Nathalie Freymond11, Françoise Thivolet12, Marianne Kambouchner13, Jean-François Bernaudin8,14, Audrey Nathalizio15, Pierre Pradat16, Paul-André Rosental2, Michel Vincent1,2,3.
Abstract
Inhalation of mineral dust was suggested to contribute to sarcoidosis. We compared the mineral exposome of 20 sarcoidosis and 20 matched healthy subjects. Bronchoalveolar lavage (BAL) samples were treated by digestion-filtration and analyzed by transmission electron microscopy. The chemical composition of inorganic particles was determined by energy-dispersive X-ray (EDX) spectroscopy. Dust exposure was also assessed by a specific questionnaire. Eight sarcoidosis patients and five healthy volunteers had a high dust load in their BAL. No significant difference was observed between the overall inorganic particle load of each group while a significant higher load for steel was observed in sarcoidosis patients (p=0.029). Moreover, the building activity sub-score was significantly higher in sarcoidosis patients (p=0.018). These results suggest that building work could be a risk factor for sarcoidosis which could be considered at least in some cases as a granulomatosis caused by airborne inorganic dust. The questionnaire should be validated in larger studies. (Sarcoidosis Vasc Diffuse Lung Dis 2018; 35: 327-332). Copyright:Entities:
Keywords: bronchoalveolar lavage; dust exposure; sarcoidosis
Year: 2020 PMID: 32476920 PMCID: PMC7170131 DOI: 10.36141/svdld.v35i4.7058
Source DB: PubMed Journal: Sarcoidosis Vasc Diffuse Lung Dis ISSN: 1124-0490 Impact factor: 0.670
Fig. 1.Flow chart showing how the dust questionnaire was scored
Subjects’ characteristics and dust load. Data are given as median (range), or n (%) unless otherwise stated
| Sarcoidosis patients (n=20) | Healthy volunteers (n=20) | P | |
| Age, years median (min-max) | 38.5 (25-48) | 33.5 (20-47) | 0.132 |
| Male gender | 14 (70) | 14 (70) | 1 |
| Region of origin | 0.009 | ||
| Europe | 11* (55) | 19 + (95) | |
| Northern Africa | 4 (20) | 1 (5) | |
| Sub-Saharan Africa | 2 (10) | 0 (0) | |
| USA | 2 (10) | 0 (0) | |
| Middle East (Iraq) | 1 (5) | 0 (0) | |
| Smoking status (pack-years) | 1 | ||
| 0-5 | 17 (85) | 17 (85) | |
| 5-10 | 2 (10) | 2 (10) | |
| >10 | 1 (5) | 1 (5) | |
| Sarcoidosis stage | - | ||
| I | 6 (30) | - | |
| II | 10 (50) | - | |
| III | 2 (10) | - | |
| IV | 2 (10) | - | |
| Building activity subscore | 6.5 (0-40) | 0 (0-27) | 0.018 |
| Overall dust load (particles/mL) | 101,611 (43,347-1,247,038) | 121,742 (57,213-260,417) | 0.589 |
| Dust exposure score | 29.5 (5-118) | 15.5 (0-75) | 0.062 |
| Specific dust load | |||
| Aluminosilicate | 56,437 (15,058-773,164) | 63,889 (29,751-190,104) | 0.530 |
| Silica | 15,655 (434-311,760) | 12,839 (4,213-32,661) | 0.328 |
| Titanium compound | 434 (434-37,411) | 2,881 (434-46,967) | 0.343 |
| Titanium oxide | 6,097 (434-68,743) | 6,042 (434-57,613) | 0.802 |
| Iron oxide | 434 (434-40,155) | 3021 (434-18,519) | 0.418 |
| Steel | 434 (434-13,749) | 434 (434-3,841) | 0.029 |
| Chromium compound | 434 (434-16,944) | 434 (434-434) | 0.075 |
| Chromium oxide | 434 (434-2,947) | 434 (434-22,634) | 0.913 |
| Aluminium compound | 434 (434-434) | 434 (434-8,230) | 0.152 |
| Talc | 434 (434-7,113) | 434 (434-6,173) | 0.970 |
* France 9, Portugal 2; + France 18, Italy 1;
Fig. 2.Mineral content in sarcoidosis patients (black dots) and healthy volunteers (grey dots). Ti comp=titanium compound, Cr= chromium, Al=aluminium