Use of routinely collected data on trihalomethane in drinking water for epidemiological purposes
T Keegana, H Whitakerb, M J Nieuwenhuijsena b, M B Toledanob, P Elliottb, J Fawelld, M Wilkinsonc, N Bestb
a The TH Huxley School
of the Environment, Earth Sciences and Engineering, Imperial College of
Science Technology and Medicine, RSM Prince Consort Road, London
SW7 2BP, UK, b Small
Area Health Statistics Unit, Department of Epidemiology and Public
Health, Imperial College of Medicine at St Mary's, London W2 1PG,
UK, c North West
Water, Thirlmere House, Lingley Mere, Great Sankey, Warrington
WA5 3LP, UK, d Warren Associates, 8 Prince Maurice Court,
Devizes, Wiltshire SN10 2RT, UK
Correspondence to: Dr M J Nieuwenhuijsen m.nieuwenhuijsen{at}ic.ac.uk
Accepted 14 March 2001
OBJECTIVES
To explore
the use of routinely collected trihalomethane (THM) measurements for
epidemiological studies. Recently there has been interest in the
relation between byproducts of disinfection of public drinking water
and certain adverse reproductive outcomes, including stillbirth,
congenital malformations, and low birth weight.
METHOD
Five years of
THM readings (1992-6), collected for compliance with statutory limits,
were analysed. One water company in the north west of England, divided
into 288 water zones, provided 15 984 observations for statistical
analysis. On average each zone was sampled 11.1 times a year. Five
year, annual, monthly, and seasonal variation in THMs were examined as
well as the variability within and between zones.
RESULTS
Between 1992 and 1996 the total THM (TTHM) annual zone means were less than half the
statutory concentration, at approximately 46 µg/l. Differences in
annual water zone means were within 7%. Over the study period, the
maximum water zone mean fell from 142.2 to 88.1 µg/l. Mean annual
concentrations for individual THMs (µg/l) were 36.6, 8.0, and 2.8 for
chloroform, bromodichloromethane (BDCM), and dibromochloromethane
(DBCM) respectively. Bromoform data were not analysed, because a high
proportion of the data were below the detection limit. The correlation
between chloroform and TTHM was 0.98, between BDCM and TTHM 0.62, and
between DBCM and TTHM
0.09. Between zone variation was larger than
within zone variation for chloroform and BDCM, but not for DBCM. There
was only little seasonal variation (<3%). Monthly variation was found
although there were no consistent trends within years.
CONCLUSION
In an area
where the TTHM concentrations were less than half the statutory limit
(48 µg/l) chloroform formed a high proportion of TTHM. The results of
the correlation analysis suggest that TTHM concentrations provided a
good indication of chloroform concentrations, a reasonable indication
of BDCM concentrations, but no indication of DBCM. Zone means were
similar over the years, but the maximum concentrations reduced
considerably, which suggests that successful improvements in treatment
have been made to reduce high TTHM concentrations in the area. For
chloroform and BDCM, the main THMs, the component between water zones
was greater than variation within water zones and explained most of the
overall exposure variation. Variation between months and seasons was
low and showed no clear trends within years. The results indicate that
routinely collected data can be used to obtain exposure estimates for
epidemiological studies at a small area level.
Keywords: chlorination byproducts; exposure; birth outcomes; routine data; trihalomethanes
© 2001 by Occupational and Environmental Medicine
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