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Background: Our primary endpoint was to use nasal cytology to compare woodworkers with unexposed subjects to see if wood dust exposure correlates with specific patterns of inflammatory or infectious rhinitis. A secondary endpoint was to identify any differences in the exposed group's nasal symptoms or nasal cytology by years of exposure or personal exposure levels. Methods: Ninety-two woodworkers and 90 controls were assessed using a questionnaire and nasal cytology (on nasal mucosa obtained by scraping). Wood dust exposure was investigated using personal sampling methods. Results: Woodworkers reported significantly more nasal symptoms than controls (p < 0.00001). The woodworkers' nasal smears revealed more neutrophils (p = 0.001) and significantly higher mean neutrophil scores (p = 0.001) than control smears. Lymphocytes were also found more often in the woodworkers' rhinocytograms (statistical trend, p = 0.06). Neutrophilic rhinitis was diagnosed more frequently in the exposed workers than in controls (chi-square = 5.97, p < 0.05). Woodworkers with lymphocytes in their nasal smears had been exposed to wood dust for longer periods of time (statistical trend; p = 0.06). No differences in nasal symptoms or cell counts emerged when woodworkers were stratified by levels of personal exposure. Conclusion: Nasal cytology should be further investigated in woodworkers before considering it a screening method for identifying woodworkers with chronic inflammatory rhinitis.

Questionnaire of etiological evaluation for tuns. (DOCX 94 kb)

Current occupational exposure levels to benzene are reduced by three orders of magnitudo (from ppm to ppb) as compared to the past. As benzene toxicity is related to its biotransformation and bioactivation pathways seem to be more active at lower exposure levels, observed effects could be higher than expected. Although the genetic polymorphisms of relevant and functional metabolic enzymes are implied in the modulation of either the risk of adverse effects [myeloperoxidase and NAD(P)H:quinone oxidoreductase] or of the biomarkers of internal dose (glutathione S-transferases M1-1, T1-1, A1-1), they are not appliable as biomarkers of susceptibility. Among biomarkers of early effect, only the longitudinal monitoring of blood cell count seems suitable to be applied in health surveillance protocols, whereas the use of biomarkers of genotoxic effect at current exposure levels is at the present not supported by literature data.

After emphasizing the characteristics of the sector and the difficulty of applying traditional industrial hygiene methods for assessing exposure to chemical agents in the construction industry, we have reviewed the major experiences of environmental and biological monitoring that can be derived from the literature. Although the determination of exposure through environmental measures should be considered the most appropriate instrument, it should be paid for the study of specific activities, while it is preferable in many situations the use of simplified tools (such as algorithms and databases) that allow the risk estimation and enable the adoption of safe work procedures and environmental and individual protection devices.

Objectives: Recently published works showed that occupational exposure to antineoplastic drugs (ANPD) is still frequent in hospital settings, despite significant safety policy improvements. The aim of this study was to assess the current level of occupational exposure to ANPD and any potentially associated cytogenetic damages in hospital nurses routinely handling ANPD. Methods: Occupationally ANPD-exposed (n = 71) and ANPD-unexposed (n = 77; control) nurses were recruited on a voluntary basis from five hospitals in Northern and Central Italy. Evaluation of surface contamination and dermal exposure to ANPD was assessed by determining cyclophosphamide (CP) on selected surfaces (wipes) and on exposed nurses’ clothes (pads). The concentration of unmetabolized CP—as a biomarker of internal dose—was measured in end-shift urine samples. Biomonitoring of genotoxic effects (i.e., biological effect monitoring) was conducted by analyzing micronuclei (MN) and chromosome aberrations (CA) in peripheral blood lymphocytes. Genetic polymorphisms for enzymes involved in metabolic detoxification (i.e., glutathione S-transferases) were analyzed as well. Results: We observed a significant increase in MN frequency (5.30 ± 2.99 and 3.29 ± 1.97; mean values ± standard deviation; p

This study aimed to correlate environmental sevoflurane levels with urinary concentrations of sevoflurane (Sev-U) or its metabolite hexafluoroisopropanol (HFIP) in order to assess and discuss the main issues relating to which biomarker of sevoflurane exposure is best, and possibly suggest the corresponding biological equivalent exposure limit values. Individual sevoflurane exposure was measured in 100 healthcare operators at five hospitals in north-east Italy using the passive air sampling device Radiello ® , and assaying Sev-U and HFIP concentrations in their urine collected at the end of the operating room session. All analyses were performed by gas chromatography-mass spectrometry. Environmental sevoflurane levels in the operating rooms were also monitored continuously using an infrared photoacoustic analyzer. Our results showed very low individual sevoflurane exposure levels, generally below 0.5 ppm (mean 0.116 ppm; range 0.007–0.940 ppm). Sev-U and HFIP concentrations were in the range of 0.1–17.28 μg/L and 5–550 μg/L, respectively. Both biomarkers showed a statistically significant correlation with the environmental exposure levels (Sev-U, r = 0.49; HFIP, r = 0.52), albeit showing fairly scattered values. Sev-U values seem to be influenced by peaks of exposure, especially at the end of the operating-room session, whereas HFIP levels by exposure on the previous day, the data being consistent with the biomarkers’ very different half-lives (2.8 and 19 h, respectively). According to our results, both Sev-U and HFIP are appropriate biomarkers for assessing sevoflurane exposure at low levels, although with some differences in times/patterns of exposure. More work is needed to identify the best biomarker of sevoflurane exposure and the corresponding biological equivalent exposure limit values.

The frequency of chromosome aberrations (CA) and micronuclei (MN) was investigated in the peripheral lymphocytes of workers occupationally exposed to low or very low concentrations of benzene. The study included 43 exposed workers (all males), namely 19 fuel-tanker drivers and 24 filling-station attendants, and 31 male subjects with no occupational exposure to the toxicant (controls). Benzene exposure was verified by means of environmental monitoring with passive personal samplers (Radiello ® ), and through biological monitoring, i.e. by measurement of urinary trans , trans -muconic acid, S -phenylmercapturic acid and benzene. The frequency of CA and MN in peripheral lymphocytes was determined according to standard procedures. Exposure to benzene was found to be significantly higher for fuel-tanker drivers (median 246.6 μg/m 3 ) than for filling-station attendants (median 19.9 μg/m 3 ). Both groups had significantly higher exposure than controls (median 4.3 μg/m 3 ). No increased frequency of CA and MN was observed in either fuel-tanker drivers or filling-station attendants compared with controls. In all subjects examined as a single group, the frequency of MN was significantly dependent on age. Only in the fuel-tanker drivers was the frequency of MN found to depend not only on age, but also on exposure to benzene. In conclusion, the frequency of MN, but not of CA, could be influenced by exposure to benzene concentrations of up to one order of magnitude lower than the threshold limit value (time-weighted average).