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. 2000 Jun 3;320(7248):1541.

Health effects of landfill sites

Whether results are assertions or evidence is unclear

Dave Roberts 1,2, Andy Redfearn 1,2, Jenny Dockerty 1,2
PMCID: PMC1118121  PMID: 10877586

Editor—Fielder et al reported increased rates of congenital malformations in the area surrounding the Nant-y-Gwyddon landfill site, having examined five “exposed” wards and 22 comparison wards.1 They imply that their findings are relevant to landfill sites receiving domestic, commercial, and industrial waste in general rather than being specific to the Nant-y-Gwyddon site.

Studies such as this are subject to several scientific constraints.2 Paramount among these are that comparison populations should not be exposed to potential risks from landfill sites and that exposed areas should be relatively unaffected by alternative potential pollutant sources.

Examination of site licence records suggests that there are up to seven other operating or closed landfill sites whose zones of potential influence include the comparison wards, including sites receiving similar wastes to the Nant-y-Gwyddon site. Given the absence of comment from the authors, we conclude that these sites are not having any measurable effects. Hence the study seems to show that one landfill site may have certain health effects while seven others do not.

Health concerns have been expressed about incinerators,3 particularly the older generation of municipal waste incinerators, which operated without modern emissions controls. A former municipal waste incinerator was located about 2 km to the southeast of the exposed area. We understand that it operated from 1974 and was decommissioned in 1987. Fielder et al's study shows a peak in rates of congenital anomaly in 1988 and 1989 in the exposed wards. We further understand that an older combustion plant had operated at roughly the same location since 1916. The more recent incinerator handled the area's municipal waste before the opening of the Nant-y-Gwyddon landfill site and was apparently closed because of local complaints, poor performance, and air pollution.

The incinerator was located in a steep northwesterly valley running through the exposed wards, and atmospheric emissions probably extended into the study area. As Fielder et al provide no direct evidence that the Nant-y-Gwyddon landfill site is the cause of the raised rates of congenital malformations, it could be equally asserted that the incinerator is a material factor, although there may be other causal factors.

We would suggest a refinement of Fielder et al's final recommendation: that protocols be developed to measure community exposures systematically in areas where raised rates of congenital anomalies have been identified. To pre-empt the findings of such exposure studies with an assumption that the cause is landfill seems to miss an important opportunity to answer the question of what causes the health effects and hence to resolve the legitimate concerns of local residents.

References

  • 1.Fielder HMP, Poon-King CM, Palmer SR, Moss N, Coleman G. Assessment of impact on health of residents living near the Nant-y-Gwyddon landfill site: retrospective analysis. [Commentary by Dolk H.] BMJ. 2000;320:19–22. doi: 10.1136/bmj.320.7226.19. . (The page range includes article and commentary.) (1 January.) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.Redfearn A, Dockerty JC, Roberts RD. Assessment of health effects associated with landfills. Wastes Management, the Scientific and Technical Review (in press).
  • 3.Friends of the Earth. Incineration campaign guide. London: FoE; 1997. [Google Scholar]
BMJ. 2000 Jun 3;320(7248):1541.

Analyses require high quality data

Judith Greenacre 1, Margery Morgan 1, David Tucker 1

Editor—We are founders of the Welsh Congenital Anomaly Register and Information Service (CARIS) and are well aware of the difficulties with congenital anomaly data mentioned by Fielder et al and by Dolk in her commentary on their paper.1-1 Analysis of our first year's data (1998) has confirmed the suspicion of previous substantial underreporting to the national congenital anomaly monitoring system.1-2

As the Welsh service has data only from 1998 and numbers are small, we are unable to reproduce Fielder et al's study concerning midline abdominal wall defects. We can, however, report the numbers of cases of all anomalies reported in 1998 for the wards surrounding the Nant-y-Gwyddon landfill site, the 22 control wards used in the study, Rhondda Cynon Taf Unitary Authority (in which the landfill site is situated), and Wales as a whole (table). We excluded data on spontaneous fetal losses from the analysis as miscarriages were not included in Fielder et al's study.

Table.

Total births and numbers of babies and fetuses reported to be affected by congenital anomalies in Wales, Rhondda Cynon Taf Unitary Authority, wards surrounding Nant-y-Gwyddon landfill site, and 22 control wards in 1998. Figures are numbers except where stated otherwise

Area Babies and fetuses considered
Cases of congenital anomaly reported to CARIS (excluding spontaneous fetal losses)
% of babies and fetuses affected
All births reported by ONS Births and terminations with congenital anomaly Terminations of pregnancy Live births Stillbirths All cases
Wales 33 610 33 798 188 609 24 821 2.43
Rhondda Cynon Taf 2 824 2 840 16 39 1 56 1.97
Nant-y-Gwyddon wards 253 256 3 3 0 6 2.34
Control wards 1 349 1 356 7 17 0 24 1.77

ONS=Office for National Statistics. 

CARIS=Welsh Congenital Anomaly Register and Information Service. 

Our data suggest a slightly higher overall prevalence of cases of congenital anomaly among babies and fetuses of women living in wards surrounding the landfill site than in both the control wards and Rhondda Cynon Taf Unitary Authority. Nevertheless, the percentage of babies and fetuses affected by congenital anomaly in the wards surrounding the Nant-y-Gwyddon landfill site is no higher than that reported overall for Wales. None of the differences found reached significance with χ2 testing. The situation should become clearer as further years of data are collected.

Fielder et al's study refers to both actual cases of congenital anomaly and anomaly rates without clearly differentiating between these terms. The Welsh service defines a case as a baby or fetus and an anomaly as the defects detected in the case. Thus the numbers of cases and numbers of anomalies in a given population may be different. In Fielder et al's study, based on data from the Office for National Statistics, this difference may not be significant as the Office for National Statistics reports 1.2 anomalies per case.1-3 In 1998, however, the Welsh service reported an average of 2.5 anomalies per case for Wales.1-2 In the future it will be important to distinguish between numbers of cases and numbers of anomalies so that equivalent comparisons can be ensured.

References

  • 1-1.Fielder HMP, Poon-King CM, Palmer SR, Moss N, Coleman G. Assessment of impact on health of residents living near the Nant-y-Gwyddon landfill site: retrospective analysis [with commentary by H Dolk] BMJ. 2000;320:19–22. doi: 10.1136/bmj.320.7226.19. . (1 January.) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 1-2.Congenital Anomaly Register and Information Service for Wales. Annual report 1998. Swansea: CARIS; 1998. [Google Scholar]
  • 1-3.Office for National Statistics. Congenital anomaly statistics 1997. London: ONS; 1997. . (MB3 No 12.) [Google Scholar]

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