Environmental Engineering Reference
In-Depth Information
London/1999/children
5-14 years [284]
Trafic at centroid of post code of
residence (GIS)
Emergency hospital visits
for asthma and
respiratory illness
No association between residence
within 150 m of main road or
trafic volume and respiratory
admission
Case-control (nonrespiratory, noninjury
acute admission
Simple Euclidean distance to main road
distance to main road with modeled peak/
hour of >1000 vehicles computed
(vehicle-meters/hour) on road within
radius of 150 m
All studies based on hospital admission have
potential bias related to criteria for
admission
Harvard Six Cities/2000/
all ages [121]
Factor analysis of 15 daily ambient PM
metal concentrations; selenium-coal
marker; lead-mobile source marker
Mortality, 1979-1988
“Mobile source” associated with
3.4% increased mortality; “coal”
1.1%; no increase with crustal
factor
Time series analysis with exposure
expressed as mobile source, crustal, coal
factors
Nottingham, United
Kingdom/2000/primary
and secondary schools
[285] d
One km 2 grid around each school; trafic
activity index (TAI—vehicle meters/day/
km 2 )
Current wheezing by
questionnaire
No association in ecological or
cross-sectional analyses
Ecological, cross-section, and longitudinal
data
Weak association (5% increased
odds) for persistence of wheeze
7-8 years later
Results inconclusive
Amsterdam/2001/all
ages [287]
Residence near road with >10 4 vehicles/
day
Mortality 1987-1998
Black smoke >NO 2 associated with
increased risk (BS 25% increase;
NO 2 5%) for residences with
>10 4 vehicles/day
Daily time series, black smoke, CO, and NO
highest at “trafic-inluenced” ixed
monitors
Day NO 2 , NO, black smoke, O 3 , CO, SO 2
Netherlands/2002/adults
55-69 years [197]
Long-term average exposure to ambient
pollutants based on regional background
and pollutants from local sources (nearby
streets)
Mortality 1986-1994
Black smoke and NO 2 associated
with all-cause and
cardiopulmonary mortality
Cohort study started in 1986; imbedded case
cohort (with no loss to follow-up in
sub-cohort)
Distance of homes from streets (50, 100 m)
with estimated exposure to black smoke
and NO 2
Larger effect seen with indicator of
distance lived from major road
Detailed exposure assessment with source
apportionment
Individual covariate data (smoking, diet,
etc.)
Analyses raise point that measurement error
in exposure assignment offsets beneits of
speciicity of exposure assignment; simple
distance marker more eficient e
( continued )
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