Samples

Human lung samples were collected after forensic autopsy from former workers of the asbestos plant in Cavagnolo, from a steel plant in Turin, and from the asbestos mine of Balangero. All of these activities were located in the Piedmont region (NW Italy) and are now dismissed. The cases were affected by pulmonary asbestosis, pleural plaques, pleural mesothelioma or lung cancer, and one had also silicatosis. The grade of asbestosis was established according to Craighead et al. (1982) [1]. Some of the Cases under investigation are summarized in the Table below. Other will be acquired and studied in the course of the project.

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Case

 

 

 Age

 

 

Sex

 

 

Occupation

 

 

Exposure

period

 

Exposure

nature

 

Diagnosis

 

 

AB count

(/g_dw*)

 

A

 

 

81

 

 

M

 

 

Asbestos

Plant

 

27 years

 

 

Crocidolite

 

 

AS (grade 3)

PP and MM

 

~3.6·10^5

 

 

B

 

 

80

 

 

F

 

 

Asbestos

plant

 

unknown

 

 

Crocidolite

 

 

AS (grade 4)

PP and LC

 

~1.2·10^7

 

 

C

 

 

80

 

 

M

 

 

Steel plant

 

 

unknown

 

 

Under

investigation

 

AS (grade 4)

MM, PP

 

~3.4·10^4

 

 

D

 

 

87

 

 

M

 

 

Asbestos

mine

 

35

 

 

Chrisotyle

 

 

AS (grade 4)

MM, PP, SS

 

~5.6·10^4

 

 

E

 

unknown

 

F

 

Textile Mill

plant

18

 

Under

investigation

AS

MM, PP

Under

investigation

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AB: Asbestos Bodies; AS: Asbestosis; PP: pleural plaques; MM: mesothelioma; LC: lung cancer; SS: silicatosis.

*g_dw: grams of dry weight tissue

 

Samples' preparation

Lung samples were preserved in formalin (10%) until non-neoplastic portions (0.25 g) of lung tissue were digested in 30 mL sodium hypochlorite solution (NaClO, reagent grade, chlorine content 10-15%, Merck) to dissolve the organic matrix. The suspension of inorganic material was filtered through mixed cellulose esters porous membranes (pore size 0.45 µm, Millipore) to recover the asbestos bodies. The membranes were then thoroughly washed with warm (40°C) deionized water to dissolve NaCl crystals formed during digestion, and finally air-dried.

Further portions of non-neoplastic lung tissues were collected to prepare 3 micron thick histological sections with a microtome. The sections were embedded in paraffin, fixed on standard microscope slides, and then stained with haematoxylin and eosin, according to the standard protocol [2], for histological examination. Lung samples were examined to estimate the number of absestos bodies by optical microscope (Leica DMLB) and SEM (Cambridge Stereoscan S360). According to the international standard, the concentration of absestos bodies was expressed as their number per gram of dry weight (gdw). This quantity was derived following the procedure described in Belluso et al. (2006) [3]: (i) the whole membrane was observed by optical microscopy at 400x magnifications, and (ii) a portion of filter representing 0.7% of its total area (about 2 mm^2) was observed by SEM at 2000x magnifications. The equivalent dry weight was calculated by dehydrating 2.5g of wet tissue of each specimen at 60°C for 3 days. In both specimens the burden of AB largely exceeded the amount established by the European Respiratory Society guidelines (10^3/gdw) to indicate a high level of occupational exposure to asbestos [4].

Due to the difficulty of locating the asbestos bodies in the histological sections, a laser micro-dissector was used to cut small areas (100 micron in diameter) of paraffin-embedded histological sections centred on the asbestos body. The fragments of lung tissue with one or more asbestos bodies inside were used for synchrotron tomography experiments. The principle of the laser-dissection procedure is described in the Figure below.

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