House dust has been consistently shown to be a primary route
of exposure to numerous environmental contaminants, in particular
pesticides, lead and other metals, and allergens, and as a surrogate
measure of exposure to these contaminants. These contaminants
are often found in greater concentrations indoors through their
accumulation from both originating indoors, and entry from outdoor
sources. This increases the potential exposure to children who
are at greater risk through: ingestion due to lower body weight
(typically 1/5 that of an adult), frequent hand-to-mouth activity
(ingesting about 2.5 times as much dust as an adult, from 10 to
1300 mg/day), and possibly enhanced uptake such as seen with lead
ingestion by children; direct inhalation, and; dermal contact
from an increased surface to volume ratio and greater body contact
with surfaces. These potential pathway sources and routes of exposures
place children and other family members at risk from exposure
to contaminants at home. Lead concentrations in house dust have
been shown correlated with particle size, although again with
inconsistent results. All of these investigations have been limited
in sample size, and have only been performed for urban locations.
Vacuum cleaner bags containing occupant collected household dust
were obtained during two prior studies covering three different
environmental areas: a rural lead mining waste superfund site
and a control (non-lead mining waste superfund area), and an urban
environment. In both studies household vacuum cleaner bags were
collected from all study participants when available (i.e. if
they had a vacuum cleaner). To investigate the variation in particle
size and associated lead concentrations, household vacuum bag
contents will be sieved into five size fractions, and each size
fraction weighed and analyzed on-site for lead content. Additionally
analysis will be performed for presence of additional metals.
The presence alone of lead in house dust as a particulate, or
as an adhesion or adsorbent to a particulate is important. But
the relationship of the contaminant concentration and/or loading
to the size fraction of the house dust and location may be a much
better indicator and surrogate for potential exposure. Fine particles
are more likely to stick to hands and be ingested or inhaled,
through hand-to-mouth behavior or close contact with source material.
Intervention measures that preferentially address a selected particle
size, surface or location may not succeed if the particle size,
surface or location is not related to the exposure of concern.
The study methodology has been designed to address some of these
issues.
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