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Perhaps, but more evidence is needed
In this issue Elliott and colleagues report on the
risks to fetuses associated with residence near landfill sites: they
compared pregnancy outcomes among British women living within 2 km of
any of 9565 landfill sites operational between 1982 and 1997 with outcomes among those who lived at least 2 km away from all known sites
(the reference area).1 They found excess risks for some adverse pregnancy outcomes, a finding consistent with previous literature, but a clear pattern of excess did not emerge and the excesses were small enough (generally less than 10%) that they could
be due to study bias, a problem that is difficult to rule out in this
type of study. Therefore, the question whether these results represent
a causal connection between residential exposures to landfill and
adverse outcomes is unresolved.
The authors found that 80% of the British population lives within 2 km
of a current or closed landfill site. This remarkable finding has
several implications. Firstly, it suggests that even small excess risks
near landfill sites would be important in public health terms.
Secondly, it raises the question of whether the reference population is
unusual, and thus whether the landfill and reference areas were
comparable in terms of other risk factors for adverse birth
outcomes This large study, based on about eight million pregnancies between 1983 and 1998, was made possible through the use of postcoded national
databases such as birth data and the National Congenital Anomaly
System. Postcoding provided a means not only of measuring distance of
residence from landfill sites but also of addressing comparability of
the two populations in terms of other risk factors for adverse
outcomes. It was found that 34% of the landfill area and 23% of the
reference area were in the most deprived third of the Carstairs
deprivation index Residence near a landfill site and excess exposure to hazardous
chemicals cannot be assumed to be equivalent. There is little published
information about the likely exposure concentrations for nearby
residents,2 although local authorities may have carried
out risk assessments.3 Contamination of water or soil may
affect a much wider population, and the impact of air dissemination may
depend on prevailing winds. Thus, if there is substantial exposure of
the population, some of the more exposed people will live more than 2 km away, and some of the less exposed within 2 km. Furthermore, since
the study was based on residence at pregnancy outcome,
misclassification could occur because women moved home between the
critical time window for exposure4 and the end of
pregnancy. Misclassification in terms of exposure or residence would
tend to cause underestimation of differences in risk between landfill
and reference populations.
Underreporting by district health authorities of anomalies among live
born and stillborn children to the National Congenital Anomaly System
is well known, and data on terminations of pregnancy for congenital
anomaly were available to the study only from 1992. Underreporting
might explain why in this study the prevalence of children needing
surgical corrections for abdominal wall defects was 40 per 10 000
births whereas the reported prevalence of these anomalies at birth or
termination was only 26 per 10 000. The important question here is
whether reporting levels for anomalies would have differed
systematically between the landfill and reference areas, thereby
biasing the results.
Uncertainty about the meaning of epidemiological results, because of
potential bias, is not resolved by arguments about statistical significance. In any case, the 99% confidence intervals quoted in the
paper are too narrow since there was no allowance for sampling error in
the reference population. However, some types of epidemiological comparison offer a stronger basis for inference than others. Evidence of an exposure-response relationship A final set of comparisons concerned the area surrounding the
5260 sites that opened in the study period: relative risks for the
population of this area compared to the reference area were calculated
both before and after the new sites opened. For most outcomes the
relative risks (landfill v reference) decreased after opening or remained the same. The exceptions were low birth weight and
neural tube defects, for which the relative risks increased by 6% and
7% respectively. These comparisons offer an alternative assessment of
the influence of landfill sites on risk without entirely solving the
problems mentioned above.
It is important that we gain a better understanding of the health
impact of different waste management options. Future studies ought to give attention to better estimates of the exposure of residents.
School of Epidemiology and Health Sciences, University of
Manchester, Manchester M13 9PT Faculty of Life and Health Sciences, University of Ulster,
Belfast BT37 0QB
for example, poor nutrition. Thirdly, the main study findings
relate to the risk of living near any sort of site, while the potential
for harm may vary greatly between sites. Higher risks associated with a
small number of sites could be lost in the overall comparison.
a classification of areas based on social class,
unemployment, access to a car, and overcrowding. All analyses were
adjusted for this difference; however, it cannot be assumed that the
three category Carstairs index is an adequate proxy measure for all
underlying risk factors. Failure to account for an unmeasured risk
factor could have artificially inflated or deflated the relative risks
for the landfill versus reference areas. For example, an absolute
difference of 10% in the prevalence of a factor that doubles risk
could increase or decrease the relative risk for landfill versus
reference areas by around 5-9%.
whereby risk increases with increasing (markers of) exposure
can be convincing. Unfortunately, further classification of the landfill group according to distance from
sites (such as <1 km and 1-2 km) was not carried out; the authors felt
that inaccuracies in the recorded location of some sites would
undermine this. An alternative approach that compared sites licensed to
receive hazardous waste and the remaining sites is probably not helpful
in this regard if, as the authors suggest, the former sites were
subject to stricter design and management.
H Dolk
| 1. |
Elliott P, Briggs D, Morris D, de Hoogh C, Hurt C, Jensen T, et al.
Risk of adverse birth outcomes in populations living near landfill sites.
BMJ
2001;
323:
363-368 |
| 2. | Vrijheid M. Health effects of residence near hazardous waste landfill sites: a review of the epidemiological literature. Environ Health Perspect 2000; 108: 101-112. |
| 3. | Environmental Agency. A practical guide to environmental risk assessment for waste management facilities. London: EA, 2000. (Guidance note 25.) |
| 4. | Wilson J. Environment and birth defects. New York: Academic Press, 1973. |
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