Children exposure to indoor ultrafine particles in urban and rural school environments

Extended exposure to ultrafine particles (UFPs) may lead to consequences in children due to their increased susceptibility when compared to older individuals. Since children spend in average 8 h/day in primary schools, assessing the number concentrations of UFPs in these institutions is important in order to evaluate the health risk for children in primary schools caused by indoor air pollution. Thus, the purpose of this study was to assess and determine the sources of indoor UFP number concentrations in urban and rural Portuguese primary schools. Indoor and outdoor ultrafine particle (UFP) number concentrations were measured in six urban schools (US) and two rural schools (RS) located in the north of Portugal, during the heating season. The mean number concentrations of indoor UFPs were significantly higher in urban schools than in rural ones (10.4 × 103 and 5.7 × 103 pt/cm3, respectively). Higher UFP levels were associated with higher squared meters per student, floor levels closer to the ground, chalk boards, furniture or floor covering materials made of wood and windows with double-glazing. Indoor number concentrations of ultrafine-particles were inversely correlated with indoor CO2 levels. In the present work, indoor and outdoor concentrations of UFPs in public primary schools located in urban and rural areas were assessed, and the main sources were identified for each environment. The results not only showed that UFP pollution is present in augmented concentrations in US when compared to RS but also revealed some classroom/school characteristics that influence the concentrations of UFPs in primary schools.

[1]  J. Sunyer,et al.  Sources of indoor and outdoor PM2.5 concentrations in primary schools. , 2014, The Science of the total environment.

[2]  Steffen Loft,et al.  Personal Exposure to Ultrafine Particles and Oxidative DNA Damage , 2005, Environmental health perspectives.

[3]  Lance Wallace,et al.  Continuous Monitoring of Ultrafine, Fine, and Coarse Particles in a Residence for 18 Months in 1999-2000 , 2002, Journal of the Air & Waste Management Association.

[4]  W. Nazaroff Indoor particle dynamics. , 2004, Indoor air.

[5]  Jarkko Tissari,et al.  Effect of wood combustion conditions on the morphology of freshly emitted fine particles. , 2014 .

[6]  A. Peters,et al.  Respiratory effects are associated with the number of ultrafine particles. , 1997, American journal of respiratory and critical care medicine.

[7]  Constantinos Sioutas,et al.  Exposure Assessment for Atmospheric Ultrafine Particles (UFPs) and Implications in Epidemiologic Research , 2005, Environmental health perspectives.

[8]  Dan Norbäck,et al.  Respiratory symptoms, perceived air quality and physiological signs in elementary school pupils in relation to displacement and mixing ventilation system: an intervention study. , 2011, Indoor air.

[9]  A. Chaloulakou,et al.  Indoor and outdoor PM mass and number concentrations at schools in the Athens area , 2007, Environmental monitoring and assessment.

[10]  L. Morawska,et al.  Children exposure assessment to ultrafine particles and black carbon: The role of transport and cooking activities , 2013 .

[11]  A. J. Ferreira,et al.  Nanoparticles, nanotechnology and pulmonary nanotoxicology. , 2013, Revista portuguesa de pneumologia.

[12]  H. Schulz,et al.  Role of oxidative stress in ultrafine particle-induced exacerbation of allergic lung inflammation. , 2009, American journal of respiratory and critical care medicine.

[13]  Lidia Morawska,et al.  Characteristics of ultrafine particle sources and deposition rates in primary school classrooms , 2014 .

[14]  U. Matson,et al.  Indoor and outdoor concentrations of ultrafine particles in some Scandinavian rural and urban areas. , 2005, The Science of the total environment.

[15]  J. Schwartz Air pollution and children's health. , 2004, Pediatrics.

[16]  N. Englert Fine particles and human health--a review of epidemiological studies. , 2004, Toxicology letters.

[17]  T. Lähde,et al.  Wood Dust Particle and Mass Concentrations and Filtration Efficiency in Sanding of Wood Materials , 2008, Journal of occupational and environmental hygiene.

[18]  Lidia Morawska,et al.  Airborne particle concentrations at schools measured at different spatial scales , 2013 .

[19]  Hanna Vehkamäki,et al.  Formation and growth rates of ultrafine atmospheric particles: a review of observations , 2004 .

[20]  Norhayati Mahyuddin,et al.  Investigating carbon dioxide in high occupancy buildings with particular application to classrooms , 2008 .

[21]  Erik Nordin,et al.  Contribution of indoor-generated particles to residential exposure , 2015 .

[22]  M. Waring,et al.  Secondary organic aerosol formation initiated from reactions between ozone and surface-sorbed squalene , 2014 .

[23]  J Pekkanen,et al.  Number concentration and size of particles in urban air: effects on spirometric lung function in adult asthmatic subjects. , 2001, Environmental health perspectives.

[24]  L. Morawska,et al.  Ultrafine particles in indoor air of a school: possible role of secondary organic aerosols. , 2009, Environmental science & technology.

[25]  L. Stanek,et al.  Attributing health effects to apportioned components and sources of particulate matter: An evaluation of collective results , 2011 .

[26]  Mike E. Davies,et al.  Impacts of energy efficiency retrofitting measures on indoor PM2.5 concentrations across different income groups in England: a modelling study , 2016 .

[27]  Tamás Weidinger,et al.  Physical properties, chemical composition, sources, spatial distribution and sinks of indoor aerosol particles in a university lecture hall , 2013 .

[28]  M G Apte,et al.  Indoor air quality, ventilation and health symptoms in schools: an analysis of existing information. , 2003, Indoor air.

[29]  S. Weichenthal,et al.  Indoor ultrafine particles and childhood asthma: exploring a potential public health concern. , 2007, Indoor air.

[30]  N. Probst-Hensch,et al.  Ambient ultrafine particle levels at residential and reference sites in urban and rural Switzerland. , 2015, Environmental science & technology.

[31]  Alan Robins,et al.  Technical challenges in tackling regulatory concerns for urban atmospheric nanoparticles , 2011 .

[32]  W G Kreyling,et al.  Long-Term Clearance Kinetics of Inhaled Ultrafine Insoluble Iridium Particles from the Rat Lung, Including Transient Translocation into Secondary Organs , 2004, Inhalation toxicology.

[33]  Matthias Ketzel,et al.  Association between short-term exposure to ultrafine particles and hospital admissions for stroke in Copenhagen, Denmark. , 2010, European heart journal.

[34]  H. Schulz,et al.  Effects of ultrafine carbon particle inhalation on allergic inflammation of the lung. , 2006, The Journal of allergy and clinical immunology.

[35]  Jonathan I Levy,et al.  Influence of traffic patterns on particulate matter and polycyclic aromatic hydrocarbon concentrations in Roxbury, Massachusetts , 2003, Journal of Exposure Analysis and Environmental Epidemiology.

[36]  H. Frommea,et al.  Particulate matter in the indoor air of classrooms — exploratory results from Munich and surrounding area , 2006 .

[37]  M. Pereira,et al.  Assessment of ultrafine particles in Portuguese preschools: levels and exposure doses. , 2014, Indoor air.

[38]  M. Pinto,et al.  Exposure of Children to Ultrafine Particles in Primary Schools in Portugal , 2015, Journal of toxicology and environmental health. Part A.

[39]  R. Britter,et al.  A review of the characteristics of nanoparticles in the urban atmosphere and the prospects for developing regulatory controls , 2010 .

[40]  I. Annesi-Maesano,et al.  Indoor Air Quality and Sources in Schools and Related Health Effects , 2013, Journal of toxicology and environmental health. Part B, Critical reviews.

[41]  P J Catalano,et al.  Using time- and size-resolved particulate data to quantify indoor penetration and deposition behavior. , 2001, Environmental science & technology.

[42]  B. Tomkins,et al.  Development and Application of Protocols for the Determination of Response of Real-Time Particle Monitors to Common Indoor Aerosols , 2004, Journal of the Air & Waste Management Association.

[43]  Y Zhu,et al.  Characterizing ultrafine particles and other air pollutants at five schools in South Texas. , 2012, Indoor air.

[44]  B. Kolarik,et al.  Exposure to ultrafine particles in relation to indoor events and dwelling characteristics , 2014 .

[45]  William W. Nazaroff,et al.  Cleaning products and air fresheners: exposure to primary and secondary air pollutants , 2004 .

[46]  Alireza Afshari,et al.  Measurement of Ultrafine Particles: A Comparison of Two Handheld Condensation Particle Counters , 2004 .

[47]  Jørn Toftum,et al.  Ultrafine particles: exposure and source apportionment in 56 Danish homes. , 2013, Environmental science & technology.

[48]  Kiyoung Lee,et al.  Indoor air quality differences between urban and rural preschools in Korea , 2011, Environmental science and pollution research international.