Published January 15, 2013 | Version v1
Journal article

Canadian House Dust Study: Population-based concentrations, loads and loading rates of arsenic, cadmium, chromium, copper, nickel, lead, and zinc inside urban homes

  • 1. Department of Earth Sciences, University of Ottawa, 140 Louis Pasteur, Ottawa, ON, Canada K1N 6N5 (Canada)
  • 2. Exposure and Biomonitoring Division, Healthy Environments and Consumer Safety Branch, Health Canada, 50 Colombine Driveway, Ottawa, ON, Canada K1A 0K9 (Canada)
  • 3. Regions and Programs Branch, Health Canada, 180 Queen Street West, Toronto, ON, Canada M5V 3L7 (Canada)
  • 4. Contaminated Sites Division, Healthy Environments and Consumer Safety Branch, Health Canada, 269 Laurier Ave West, Ottawa, ON, Canada K1A 0K9 (Canada)

Description

The Canadian House Dust Study was designed to obtain nationally representative urban house dust metal concentrations (μg g−1) and metal loadings (μg m−2) for arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), nickel (Ni), lead (Pb), and zinc (Zn). Consistent sampling of active dust of known age and provenance (area sampled) also permitted the calculation of indoor loading rates (mg m−2 day−1 for dust and μg m−2 day−1 for metals) for the winter season (from 2007 to 2010) when houses are most tightly sealed. Geomean/median indoor dust loading rates in homes located more than 2 km away from industry of any kind (9.6/9.1 mg m−2 day−1; n = 580) were significantly lower (p < .001) than geomean (median) dust loading rates in homes located within 2 km of industry (13.5/13.4 mg m−2 day−1; n = 421). Proximity to industry was characterized by higher indoor metal loading rates (p < .003), but no difference in dust metal concentrations (.29 ≥ p ≤ .97). Comparisons of non-smokers' and smokers' homes in non-industrial zones showed higher metal loading rates (.005 ≥ p ≤ .038) in smokers' homes, but no difference in dust metal concentrations (.15 ≥ p ≤ .97). Relationships between house age and dust metal concentrations were significant for Pb, Cd and Zn (p < .001) but not for the other four metals (.14 ≥ p ≤ .87). All seven metals, however, displayed a significant increase in metal loading rates with house age (p < .001) due to the influence of higher dust loading rates in older homes (p < .001). Relationships between three measures of metals in house dust – concentration, load, and loading rate – in the context of house age, smoking behavior and urban setting consistently show that concentration data is a useful indicator of the presence of metal sources in the home, whereas dust mass is the overriding influence on metal loadings and loading rates. - Highlights: ► The Canadian House Dust Study is a nationally representative random sample. ► Dust was collected from 1025 urban homes from 13 cities with population > 100,000. ► Typical indoor dust and metal loading rates and metal concentrations are reported. ► Dust mass is the overriding influence on metal loadings and loading rates. ► This population-scale study contributes to defining the exposome

Availability note (English)

Available from http://dx.doi.org/10.1016/j.scitotenv.2012.11.003

Additional details

Identifiers

DOI
10.1016/j.scitotenv.2012.11.003;
PII
S0048-9697(12)01420-9;

Publishing Information

Journal Title
Science of the Total Environment
Journal Volume
443
Journal Page Range
p. 520-529
ISSN
0048-9697
CODEN
STENDL

INIS

Country of Publication
Netherlands
Country of Input or Organization
International Atomic Energy Agency (IAEA)
INIS RN
45098433
Subject category
S54: ENVIRONMENTAL SCIENCES;
Descriptors DEI
ARSENIC; CADMIUM; CANADA; CHROMIUM; CONCENTRATION RATIO; COPPER; DUSTS; ECOLOGICAL CONCENTRATION; HOUSES; LEAD; LOADING RATE; NICKEL; TOBACCO SMOKES; ZINC
Descriptors DEC
AEROSOLS; BUILDINGS; COLLOIDS; DEVELOPED COUNTRIES; DIMENSIONLESS NUMBERS; DISPERSIONS; ELEMENTS; METALS; NORTH AMERICA; RESIDENTIAL BUILDINGS; RESIDUES; SEMIMETALS; SMOKES; SOLS; TRANSITION ELEMENTS

Optional Information

Copyright
Copyright (c) 2012 Elsevier Science B.V., Amsterdam, The Netherlands, All rights reserved.