A pilot risk assessment study of strontium chromate among painters in the aeronautical industry.

OBJECTIVE: A method for risk assessment of occupational exposure to strontium chromate (SrCrO4) in painters employed in the aeronautical industry is described. METHODS: Assessment was made of 21 male workers of the painting division, potentially exposed to SrCrO4 (exposed), and 20 male workers of the tests and warehouse divisions (controls). All participants completed a questionnaire about work tasks, lifestyle habits, hobbies and diet. Personal active sampling for the determination of Cr and Sr was performed both during paint-spraying and during other operations in the painting division area. On the same day as environmental sampling, urine samples were collected at the beginning and end of the work shift in exposed workers to determine urinary chromium (CrU), and only at the end of the shift in controls. In the second half of the shift, a blood sample was taken in 10 exposed workers and 10 controls, to determine Cr in plasma (CrP) and in red blood cells (CrRBC). RESULTS: During paint-spraying, Cr concentrations ranged between 1.38 and 17.10 microg/m3, versus 0.02 to 0.07 microg/mi in the painting division area, while the Sr concentration was 22.90 microg/m3 in the paint-spray booth versus 0.07 microg/m3 in the painting division area. CrU at the end of the work shift, CrP and CrRBC, did not show significant differences between exposed workers and controls. Moreover, in exposed workers there were no differences between CrU measured at the beginning and at the end of the work shift. CONCLUSIONS: This approach, consisting of simultaneous environmental and biological monitoring, suggested no absorption of chromium in the painters thanks to the efficacy of the technical, organizational and personal protection measures adopted. However, the evident exposure to high levels of SrCrO4 during paint-spraying highlights how absolutely essential it is to ensure strict compliance with all the preventive measures foreseen by the EU and national regulations for occupational exposure to carcinogens.

Environmental factors affecting the urinary excretion of inorganic arsenic in the general population.

OBJECTIVE: To assess the critical issues concerning the use of urinary inorganic arsenic (iAs), including As3, As5, monomethylarsonic acid (MMA) and dimethylarsinic acid (DMA), as biomarker of internal dose in order to monitor environmental and occupational exposure to inorganic As, considering the influence of diet and drinking water on excretion of iAs. METHODS: The design protocol stipulated collection of weekly urine samples from 6 male subjects for 5 consecutive months. In all the urine samples, iAs was determined by Hydride Generation-Atomic Absorption Spectrophotometry (HG-AAS). In the subjects with iAs higher than 35 microg/L, Biological Exposure Index (BEI) proposed by the American Conference of Governmental Industrial Hygienists (ACGIH), urinary arsenic speciation was performed by HPLC-ICP-MS. Exposure to airborne As was evaluated monthly using personal environmental samplers worn for 8 hours. Throughout the study, the participants filled out a daily food diary, also detailing types of water drunk. RESULT: Exposure to airborne As was invariably below the limit of detection, equal to 1 ng/m3. A total of 77 urine samples were collected. iAs was always detectable and was higher in 7 urine samples, obtained from 5 of the 6 subjects examined, than the BEI. Among foods with a high As content, the intake of seafood and fish within 72 hours before providing the sample seems to be the principal source of the iAs concentrations, while the intake of rice or drinking water showed no influence on this biological marker. Instead, drinking wine within 24 hours before urine sample collection can cause a significant increase in the excretion of iAs. CONCLUSIONS: In populations that eat large amounts of fish and seafood, the use of iAs to monitor occupational and environmental exposure to inorganic As seems to present some problems, and urinary As speciation may be essential at least in cases with As measurements above the biological limit values. In any case, a diet sheet reporting all foods eaten within 3 days of urine collection seems to be an indispensable tool to ensure a correct interpretation of the results.

[Health risk assessment of exposure to metals in the workers of the steel foundry and in the general population of Taranto (Italy)]. / Valutazione del rischio per la salute do esposizione a elementi metallici nei lavoratori del siderurgico e nella popolazione generale di Taranto (Italia).

OBJECTIVE: To study the urinary excretion of As, Cr, Mn, Co, Ni, Cu, Zn, Cd, Sn, Ba, Hg, Pb, Sb in workers at the Taranto integrated-cycle steel foundry and in subjects from the general population of Taranto, to assess the health risk posed by occupational exposure and environmental exposure, respectively, to these metals. MATERIALS AND METHODS: The study included 49 steel foundry workers (exposed), working in the minerals and agglomerates pools, steel processing plants 1 and 2 and maritime plants, and 50 subjects belonging to the general population of Taranto resident at various distances from the factory (controls), randomly selected from the exposed subjects and controls enrolled in previous research conducted in 2005. A questionnaire was administered to all participants, enquiring into general characteristics, lifestyle, diet, and any medical conditions. Informed written consent to take part in the study was obtained from all subjects before enrolment. The results of environmental monitoring performed in 2005 in the workers' sectors, consisting of determining As, Cr, Mn, Ni, Cu, Zn, Cd and Pb in the respirable dust, revealed by both samplers applied in fixed positions and personal samplers, were considered. Urine samples were obtained from all participants on a Friday, to determine As and Cr by AAS and all the other metal elements by a multielement technique with ICP-MS. Urinary creatinine was also determined to make any necessary adjustments. All urine analyses were performed in 2005 within one month of urine collection. RESULTS: In the respirable dust, As and Cd were always within the LOD, whereas Cr, Mn, Ni, Cu and Pb were 1-2 orders of magnitude below the respective TLV-TWA of the ACGIH. Mn was the only metal element that presented significantly higher urinary concentrations in exposed subjects as compared to controls, although the values in both groups were in any case within the Italian reference range. Co, Cu, Zn, Sn and Sb showed significantly higher urinary concentrations in controls than in the exposed subjects, while there were no differences in As, Cr, Cd, Ba, Hg and Pb between the two groups. Ni was within the LOD in the 60% of the subjects in the two groups. Multiple stepwise regression showed a dependence of Cr on age, of As on the number of days since the last meal of mollusks and crustaceans, of Zn on the consumption of mollusks, and of Cd and Pb on smoking expressed as the number of pack/year. DISCUSSION: The research did not reveal higher urinary excretion of the metal elements in the steelworkers than in the subjects from the general population of Taranto resident at different distances from the factory, except for Mn, that was anyway within the reference range. This allows us to consider that there is no relevant health risk posed by occupational exposure to metal elements in the steelworkers, nor by environmental exposure to the same elements in the residents of the city of Taranto. In particular, no pollution of the living environment by metal elements of industrial origin was demonstrated, whereas other non occupational factors seem to condition the intake of these metal elements.