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In tunnel construction work, dust is generated from rock drilling, rock bolting, grinding, scaling, and transport operations. Other important dust-generating activities are blasting rock and spraying wet concrete on tunnel walls for strength and finishing work. The aim of this study was to identify determinants of dust exposure in tunnel construction work and to propose control measures. Personal exposures to total dust, respirable dust, and alpha-quartz were measured among 209 construction workers who were divided into 8 job groups performing similar tasks: drill and blast workers, shaft drilling workers, tunnel boring machine workers, shotcreting operators, support workers, concrete workers, outdoor concrete workers, and electricians. Information on determinants was obtained from interviewing the workers, observation by the industrial hygienist responsible for the sampling, and the job site superintendent. Multivariate regression models were used to identify determinants associated with the dust exposures within the job groups. The geometric mean exposure to total dust, respirable dust, and alpha-quartz for all tunnel workers was 3.5 mg/m(3) (GSD = 2.6), 1.2 mg/m(3) (GSD = 2.4), and 0.035 mg/m(3) (GSD = 5.0), respectively. A total of 15 percent of the total dust measurements, 5 percent of the respirable dust, and 21 percent of the alpha-quartz exceeded the Norwegian OELs of 10 mg/m(3), 5 mg/m(3), and 0.1 mg/m(3), respectively. Job groups with highest geometric mean total dust exposure were shotcreting operators (6.8 mg/m(3)), tunnel boring machine workers (6.2 mg/m(3)), and shaft drilling workers (6.1 mg/m(3)). The lowest exposed groups to total dust were outdoor concrete workers (1.0 mg/m(3)), electricians (1.4 mg/m(3)), and support workers (1.9 mg/m(3)). Important determinants of exposure were job group, job site, certain tasks (e.g., drilling and scaling), the presence of a cab, and breakthrough of the tunnel. The use of ventilated, closed cabs appeared to be the single most important control measure for lowering exposures.
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http://dx.doi.org/10.1080/10473220290096032 | DOI Listing |
Thorax
March 2025
Department of Occupational & Environmental Health, School of Public Health, Tongji Medical College, Huazhong University of Science and Technology, Wuhan, Hubei, China
Background: High-level exposure to crystalline silica dust is the key factor in silicosis. Long-term exposure to low-level silica dust, for example, lower than that in occupational exposure limits, still needs to be studied for their risk of silicosis.
Methods: A total of 30 697 workers were included from a cohort in China.
Sci Total Environ
March 2025
Uppsala University, Department of Medical Science, Occupational and Environmental Medicine, University Hospital, 75185 Uppsala, Sweden. Electronic address:
Objective: Few studies have investigated links between fraction exhaled nitric oxide (FeNO), the home and the school environment. FeNO is a biomarker of T helper 2 (Th2) airway inflammation. We investigated associations between FeNO and airway symptoms, allergies, household and classroom exposure among pupils in ten primary schools in Stockholm (N = 415).
View Article and Find Full Text PDFInt Forum Allergy Rhinol
March 2025
Department of Immunopathology, Division of Biomedical Science, Faculty of Medicine, Medical University of Lodz, Lodz, Poland.
Background: House dust mites (HDMs) are the most common cause of atopic sensitivities and allergic diseases worldwide. Therefore, we decided to conduct a meta-analysis of randomized clinical trials to evaluate the effect of different methods of HDM avoidance.
Methods: PubMed, Web of Science, and the Cochrane Central Register of Controlled Trials databases were searched to find articles of control-compared randomized clinical trials, which investigated the following analyzed outcomes: total amount of dust (g); Der1 (Der p1 plus Der f1) concentrations (µg/g); Der p1 concentrations (µg/g); Der p2 concentrations (µg/g); Der f1 concentrations (µg/g); measurements of peak expiratory flow (PEF) (L/min); respiratory, pulmonary, or nasal symptoms according to various scales, including visual analog scale; exacerbations; Asthma Control Questionnaire score measurements; and change in quality of life scales (overall change, activity change, symptom change, and emotional function change).
Sci Total Environ
March 2025
Laboratoire National de Santé (LNS), Department of Health Protection, Unit Environmental Hygiene and Human Biological Monitoring, 1, Rue Louis Rech, L-3555 Dudelange, Luxembourg; Environment and Health, Department of Public Health and Primary Care, KU Leuven, Leuven, Belgium. Electronic address:
We conducted a literature review to gain insight into the European state-of-the-art of plasticizer research in indoor environments. This review focused on indoor plasticizer concentrations in the gas and sorbed phases and source material emissions. We found that indoor plasticizer exposure studies started in the year 2000.
View Article and Find Full Text PDFAllergol Immunopathol (Madr)
March 2025
Unidad de Neumología y Alergología Pediátrica, Servicio de Pediatría, Hospital Universitario de Móstoles, Madrid, Spain;
Background: The study aimed to evaluate the level of agreement between specialists in pediatric allergology regarding the diagnosis and indications for allergen immunotherapy (AIT) for dust mites, molds, animal dander, and Hymenoptera venom allergen, as well as mixtures of several allergen sources in polysensitized children in Spain.
Materials And Methods: A Delphi study was performed using an online survey designed by a committee of pediatric AIT experts: 46 and 44 panelists participated in Rounds 1 and 2, respectively. In Round 1, 204 statements on 8 dimensions were evaluated (Diagnosis, Therapeutic management, and Pollens - Part I; Mites, molds, animals, hymenoptera venom, and mixtures - Part II).
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