Spatial variability of particulates in homes: implications for infant exposure.

Personal monitoring of particulate matter (PM) exposure in infants is difficult. Indirect, microenvironment modelling methods are more practical. Infants spend most of their time indoors at home and the aim of this study was to investigate spatial variations in PM concentrations within homes. Three size fractions of PM - particles with an aerodynamic diameter of less than 10 microm (PM(10)), less than 2.5 microm (PM(2.5)) and total suspended particulates (TSP) - were monitored in the homes of 77 infants (0-2 years) using a multi-stage virtual impactor. In all homes PM was monitored simultaneously in the main living room at heights of 1.4 m and 0.2 m from the floor. In 26 of these homes monitoring was also conducted simultaneously in the infant's bedroom. Further, PM(10) was measured simultaneously in the living room, bedroom and child's cot in 14 homes using a real-time photometer. All homes in the study were non-smoking households. On average, there were no significant differences between concentrations of any of the different PM size fractions measured at the two heights (living room) and between living room and bedroom concentrations. However, there were only moderate correlations in concentrations between the different microenvironments and in some homes there was considerable variation between sampling sites. From the real-time measurements there seemed to be good agreement between concentrations measured in different rooms and in the cot and short-term peak concentrations at one sampling site were often mirrored at other sites. These results suggest that, although large variations in PM concentrations between rooms within homes can occur, a single monitoring station can provide a reasonable estimate of indoor concentrations.

[1]  Douglas W Dockery,et al.  Health effects of particulate air pollution. , 2009, Annals of epidemiology.

[2]  D. Zmirou,et al.  Can one use ambient air concentration data to estimate personal and population exposures to particles? An approach within the European EXPOLIS study. , 2001, The Science of the total environment.

[3]  J. Spengler,et al.  Room-to-Room Variations in Concentration of Respirable Particles in Residences. , 1981, Environmental science & technology.

[4]  S N Li,et al.  Evaluation of six inhalable aerosol samplers. , 2000, AIHAJ : a journal for the science of occupational and environmental health and safety.

[5]  A. Woodcock,et al.  Relationship between mite, cat, and dog allergens in reservoir dust and ambient air , 1999, Allergy.

[6]  Michal Krzyzanowski,et al.  Air pollution attributable postneonatal infant mortality in U.S. metropolitan areas: a risk assessment study , 2004, Environmental health : a global access science source.

[7]  M. Nieuwenhuijsen,et al.  The spatial and temporal variation of particulate matter within the home , 2000, Journal of Exposure Analysis and Environmental Epidemiology.

[8]  T. Moreno,et al.  The spatial and temporal variations in PM10 mass from six UK homes. , 2004, The Science of the total environment.

[9]  J D Spengler,et al.  Particle Total Exposure Assessment Methodology (PTEAM) study: distributions of aerosol and elemental concentrations in personal, indoor, and outdoor air samples in a southern California community. , 1993, Journal of exposure analysis and environmental epidemiology.

[10]  Thomas Lumley,et al.  Pulmonary Effects of Indoor- and Outdoor-Generated Particles in Children with Asthma , 2005, Environmental health perspectives.

[11]  R. W. Wiener,et al.  Use of a pilot study for designing a large scale probability study of personal exposure to aerosols. , 1991, Journal of exposure analysis and environmental epidemiology.

[12]  Shelly L. Miller,et al.  Environmental tobacco smoke particles in multizone indoor environments , 2001 .

[13]  R. Jenkins,et al.  Aerial release of bacteria from cot mattress materials and the sudden infant death syndrome , 2005, Journal of applied microbiology.

[14]  J. Colls,et al.  The Influence of Human Activity on the Vertical Distribution of Airborne Particle Concentration in Confined Environments: Preliminary Results , 1998 .

[15]  J. Corbyn Sudden infant death due to carbon dioxide and other pollutant accumulation at the face of a sleeping baby. , 1993, Medical hypotheses.

[16]  Andrea R Ferro,et al.  Outdoor Versus Indoor Contributions to Indoor Particulate Matter (PM) Determined by Mass Balance Methods , 2004, Journal of the Air & Waste Management Association.

[17]  Juan Zhang,et al.  Infant Mortality and Air Pollution: A Comprehensive Analysis of U.S. Data for 1990 , 2000, Journal of the Air & Waste Management Association.

[18]  Kerrie Mengersen,et al.  Characteristics of particle number and mass concentrations in residential houses in Brisbane, Australia , 2003 .

[19]  S. Tong,et al.  Air pollution and sudden infant death syndrome: a literature review. , 2004, Paediatric and perinatal epidemiology.

[20]  A. Woodcock,et al.  Fungal contamination of bedding , 2006, Allergy.

[21]  D. Dockery,et al.  Health Effects of Fine Particulate Air Pollution: Lines that Connect , 2006, Journal of the Air & Waste Management Association.

[22]  Alexandra Farrow,et al.  Time spent in the home by different family members , 1997 .

[23]  P. Lioy,et al.  Assessing exposures to inhaled complex mixtures. , 1993, Environmental Health Perspectives.

[24]  M. Kryger,et al.  Principles and Practice of Sleep Medicine in the Child , 1995 .

[25]  James A. Wiley,et al.  Study of children's activity patterns , 1991 .

[26]  Wolfgang Koch,et al.  Design and Performance of a New Personal Aerosol Monitor , 1999 .

[27]  C. Bearer,et al.  How are children different from adults? , 1995, Environmental health perspectives.