Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

Environmental Health Perspectives Volume 108, Supplement 1, March 2000
[Citation in PubMed] [Related Articles]

Health Effects of Residence Near Hazardous Waste
Landfill Sites: A Review of Epidemiologic Literature
Martine Vrijheid
Environmental Epidemiology Unit, Department of Public Health and Policy, London School of Hygiene
and Tropical Medicine, London, United Kingdom● Methods●

Epidemiologic Studies on Health Effects of Landfill Sites●

Conclusions●

Further Research Needs

Abstract
This review evaluates current epidemiologic literature on health effects in relation to residence near
landfill sites. Increases in risk of adverse health effects (low birth weight, birth defects, certain types ofcancers) have been reported near individual landfill sites and in some multisite studies, and althoughbiases and confounding factors cannot be excluded as explanations for these findings, they may indicate
real risks associated with residence near certain landfill sites. A general weakness in the reviewed studies
is the lack of direct exposure measurement. An increased prevalence of self-reported health symptoms
such as fatigue, sleepiness, and headaches among residents near waste sites has consistently beenreported in more than 10 of the reviewed papers. It is difficult to conclude whether these symptoms arean effect of direct toxicologic action of chemicals present in waste sites, an effect of stress and fears
related to the waste site, or an effect of reporting bias. Although a substantial number of studies havebeen conducted, risks to health from landfill sites are hard to quantify. There is insufficient exposure
information and effects of low-level environmental exposure in the general population are by their naturedifficult to establish. More interdisciplinary research can improve levels of knowledge on risks to humanhealth of waste disposal in landfill sites. Research needs include epidemiologic and toxicologic studies
on individual chemicals and chemical mixtures, well-designed single- and multisite landfill studies,development of biomarkers, and research on risk perception and sociologic determinants of ill health.
Key words: epidemiology, hazardous waste, health effects, landfill, residence, review. -- Environ Health
Perspect 108(suppl 1):101-112 (2000).
http://ehpnet1.niehs.nih.gov/docs/2000/suppl-1/101-112vrijheid/abstract.html
Address correspondence to M. Vrijheid, Environmental Epidemiology Unit, London School of Hygiene andTropical Medicine, Keppel Street, WC1E 7HT London, UK. Telephone: 44 171 927 2415. Fax: 44 171 580
4524. E-mail: m.vrijheid@lshtm.ac.uk
This work was conducted under a research fellowship from The Colt Foundation. The project was funded
specifically by the U.K. Environment Agency. The views expressed are those of the author and the

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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

Environment Agency accepts no liability for any loss or damage arising from the interpretation or use of theinformation or reliance on views contained herein. The author is grateful to H. Dolk and B. Armstrong fortheir comments on several drafts of this review.
Received 24 November 1998; accepted 7 June 1999.

The disposal of wastes in landfill sites has increasingly caused concern about possible adverse healtheffects for populations living nearby, particularly in relation to those sites where hazardous waste isdumped. Studies on the health effects of landfill sites have been carried out mainly in North America andexisting reviews focus entirely on this literature (1,2). Recent publications of large studies both in andoutside North America warrant an update of evidence presented in previous reviews. Up-to-dateknowledge about epidemiologic evidence for potential human health effects of landfill sites is important
for those deciding on regulation of sites, their siting and remediation, and for those whose task it is to
respond to concerns from the public in a satisfactory way.
We intend to present a critical discussion of all major epidemiologic studies published since 1980 on
health effects related to residence near landfill sites in North America, Europe, and elsewhere. Special
attention is paid to recent studies and studies outside the United States that have not been included inprevious reviews.

Methods
Throughout this review the term landfill is used for any controlled or uncontrolled disposal of waste toland. Relevant papers were found through computerized literature searches on MEDLINE (MEDLINE
Database, National Library of Medicine, Bethesda, MD) (www.biomednet.com) and BIDS Databases,
Joint Information Systems Committee, University of Bath, Bath, UK (www.bids.ac.uk) from 1980
through to 1998 using keywords "landfill" and "hazardous waste site." In addition, articles were traced
through references listed in previous reviews. All papers found in this manner that studied health effects
in residents near waste landfill sites and that were published in journals available through the British
Library and libraries of the University of London were included in this review. A few papers referred toin previous reviews could not be traced because they were published in local journals in the UnitedStates. Published reports of recent studies that have not yet appeared in peer-reviewed journals have been
included in the review. A few abstracts of European studies have been included, although full research
papers of these studies have not been published because they reflect growing concerns about landfill inEurope. A total of 50 papers, reports, and abstracts are reviewed in this article. Investigations of thehealth risks to those employed in the handling, transport, clean-up, or maintenance of substances atlandfill sites are very scarce and have not been included in this review. Many chemicals or groups ofchemicals potentially present in landfill sites, including organic solvents, polychlorinated biphenyls(PCBs), and heavy metals, have shown adverse effects on human health or in animal experiments. A
discussion of findings from either epidemiologic or toxicologic research on health effects related to
specific chemicals is beyond the scope of this review.

Epidemiologic Studies on Health Effects of Landfill Sites
The majority of studies evaluating possible health effects in human populations living near landfill sites
investigate communities near one specific waste disposal site (single-site studies), frequently in response
to concerns from the public about reported contamination from the site or reported clusters of disease. A
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literaturesmall number of studies have addressed the risks of living near waste sites, independent of whether thesites caused concern, by a priori specifying a number of sites for study. These will be referred to as
multisite studies. Single- and multisite studies have different methodologic problems and are therefore
discussed separately in this paper. Most individual studies are discussed in detail in this article. Where
appropriate due to common methodologic issues (e.g., in studies of self-reported health outcomes andclusters of disease) or due to a common landfill site of concern (e.g., in the Love Canal studies and Santa
Clara County studies), less emphasis was put on individual studies and more on common issues. Studies
included in the review are summarized in Table 1 (single-site studies) and Table 2 (multisite studies).
Discussion of individual single- and multisite studies is preceded by a discussion of issues common to
the interpretation of all landfill studies.
Table 1 is in a 96K pdf file. For further information on viewing pdf files, please go here.
Issues Common to the Interpretation of Landfill Studies
A general problem in epidemiologic studies of landfill sites, whether studying single or multiple sites, isthat there is insufficient information regarding potential human exposures from landfill sites. Althoughlandfill sites are numerous and widespread, very few have been evaluated with respect to both the typesof chemicals they contain and the extent to which they may be releasing chemicals. Most such work has
been conducted in the United States under the Superfund program (3). In other countries, information islargely lacking. Moreover, although chemicals have been found to migrate off site at a number of sitesthat have been thoroughly investigated (2), we know very little about the extent to which residents living
near a site are exposed to these chemicals. A few studies that have attempted to measure certain
chemicals in blood and urine of populations near waste sites have generally not found increased levels ofvolatile organic compounds (VOCs) (4), mercury (5), or PCBs (6). Because knowledge of whether and towhat extent substances from waste sites reach the human population is still largely lacking, and because
resources are rarely available to carry out extensive exposure measurements or modeling, epidemiologic
studies have based the assessment of exposure to landfills mainly on surrogate measures such as
residence in an area close to a waste site or distance of residence from a waste site. The use of suchsurrogate, indirect exposure measurements can lead to misclassification of exposure which, if notdifferent for diseased and nondiseased persons, will decrease the sensitivity of the study to find a true
effect.
In addition to being hampered by insufficient exposure data, the study of landfill exposures iscomplicated by the fact that if residential populations are exposed to chemicals from landfill sites, it will
generally be to low doses of mixtures of chemicals over long periods of time. Associations with such
low-level environmental exposures in the general population are by their nature hard to establish.
Low-dose exposures are generally expected to generate small increases in relative risk that will bedifficult to distinguish from noise effects introduced by confounding factors and biases.
In most of the landfill studies reviewed in this article, residents near waste sites are studied without
knowledge of the exact route(s) of exposure to chemicals from the site. Migration of hazardous
substances into groundwater is often an important environmental concern in relation to landfill sites,
which may represent a public health problem, especially when a site is located near aquifers supplying
public drinking water. However, in many situations the drinking water supply of residents near waste
sites does not originate from the local area. For people living in the vicinity of these sites, other routes of
exposure may be of more concern. Landfill sites may be a source of airborne chemical contamination via
the off-site migration of gases and via particles and chemicals adhered to dust, especially during the
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

period of active operation of the site. Very little is known about the likelihood of air exposure fromlandfill sites through landfill gases or dust. At some of the sites described below, low levels of volatileorganic chemicals have been detected in indoor air of homes near landfill sites (7-13), in outdoor air inareas surrounding sites (14-20) or in on-site landfill gas (21). Other possible routes of exposure include
contamination of soil, ground, and surface water, which may lead to direct contact or pollution of indoor
air in the case of evaporation of VOCs into basements of nearby houses. Contamination via the foodchain may sometimes be of concern for nearby residents in the case of consumption of home-grownvegetables. Drinking water is a possible route of exposure only if water for domestic use is locallyextracted. If this is the case, other domestic water uses (bathing, washing) may also lead to exposure via
inhalation of evaporated VOCs and/or direct contact (13).
Some issues related to specific health outcomes should be noted in both single- and multisite studies. A
general problem in studies of cancer incidence is the long latency period between exposure and clinicalmanifestation of the cancer. Studies may not always allow for a long enough latency period, which
reduces their power to pick up long-term effects. Moreover, because of the long latency period, aconsiderable number of people may have migrated into or out of the exposed areas between time of
exposure and time of diagnosis, which will lead to misclassification of exposures. Studies ofchromosome changes (chromosome aberrations and sister chromatid exchanges) are undertaken with theassumption that such changes are related to the mechanisms underlying cancer and possibly birth defects.
Chromosomal changes are studied as biomarkers of early response or effect of exposure to mutagenic
and carcinogenic chemicals. Sorsa et al. (22) point out that theoretically it is reasonable to assume thatchromosome damage is directly related to cancer etiology, but the number of agents clearly shown to
induce such damage in humans is still limited. Increased frequencies of chromosome changes may
indicate exposure to mutagens and carcinogens, but it is not clear at present how well they predict cancer
risk. Low birth weight is thought to be relatively sensitive to effects of chemical exposures (23). It is also
relatively easy to collect accurate information on birth weight from birth certificates. However, a large
number of risk factors are associated with low birth weight (including smoking, socioeconomic status,
nutritional factors, parental height) (24), and these may act as confounding factors, giving biased
estimates of association with residence close to a site. Birth defects have fewer established risk factors
than other reproductive outcomes such as low birth weight, and studies of birth defects may therefore beless affected by confounding factors, although unknown risk factors could still play a confounding role.
Also, birth defects represent an etiologically very heterogeneous set of conditions; analyses of the total
malformation rate (all defects combined) have the advantage of larger numbers but may not be sensitive
enough to pick up increases in risk of specific defects. The grouping of malformations into groups thatare etiologically similar is difficult because of lack of knowledge on causes of specific defects. Grouping
therefore always entails a compromise between large enough numbers and etiologic specificity.
Single-Site Studies
The investigation of single landfill sites has been important as a response to community concerns; manyof the single-site studies discussed below are prompted by public concerns, often under considerable
political pressure. This means that they are prone to recall and reporting biases that may weaken theinvestigations and partly explain increases in reported health outcomes. Single-site studies haveexamined a vast range of possible health outcomes, often without a specific disease hypothesis being
proposed a priori. Such "fishing expeditions" are thought to be of less scientific value than studies thatstart with a clear hypothesis (1). Including these fishing expeditions in evaluating the consistency offindings across multiple studies is important nevertheless when assessing evidence for health risks.
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

A less avoidable problem in single-site studies is that the size of populations living near waste sites
generally is small and, especially when the outcome is a rare disease, this can seriously limit thestatistical power of an investigation.
Single-site studies discussed in this section are grouped into those examining hard end points such as
cancer and reproductive outcomes, those studying self-reported health outcomes and symptoms, thosefollowing up reported clusters of disease near landfill sites with geographic comparisons of disease rates,
and those specifically investigating the contamination of well water used for drinking or other domestic
uses in relation to health effects. These last studies were discussed separately to determine whether
conclusions can be drawn about specific pathways of exposure.
Studies of cancers, reproductive outcomes, and chromosomal damage. Large quantities of toxic
materials (residues from pesticide production) were dumped at the landfill of Love Canal, New YorkState, during the 1930s and 1940s, followed by the building of houses and a school on and around thelandfill in the 1950s. By 1977 the site was leaking and chemicals were detected in neighborhood creeks,sewers, soil, and indoor air of houses. This led to one of the most widely known and publicized incidents
of environmental pollution from landfill. Exposure of Love Canal residents, although not wellunderstood, may have occurred via inhalation of volatile chemicals in home air or via direct contact withsoil or surface water (10). The drinking water supply was not contaminated. Chemicals detected at Love
Canal were primarily organic solvents, chlorinated hydrocarbons and acids, including benzene, vinyl
chloride, PCBs, dioxin, toluene, trichloroethylene, and tetrachloroethylene. Several studies wereconducted to detect whether Love Canal residents suffered adverse health effects.
Janerich et al. (7) compared cancer incidence for the Love Canal area with data for the entire state from1955 to 1977 and found no increase in cancer rates at Love Canal for any organ site. This included
leukemia, lymphoma, and liver cancer, which were thought to be the cancers most likely to result fromexposures to the chemicals found at the site. The study is limited in that no information was available on
confounding factors such as socioeconomic status and smoking. Subsequently, Heath et al. (8) compared
the frequencies of chromosome changes (sister chromatid exchanges and chromosomal aberrations) inresidents who lived in the first ring of houses adjacent to Love Canal in 1978 with those of control
persons from socioeconomically similar census tracts. No differences in frequencies of chromosome
damage were found. Chromosome changes were measured in 1981 and 1982, a few years after people
were evacuated from the first ring of houses and therefore were no longer exposed. The authors point out
that chromosome damage may be a reversible effect, which may explain the negative findings.
Infants and children have been the subject of other Love Canal studies. A cross-sectional study (9)reported an increased prevalence of seizures, learning problems, hyperactivity, eye irritation, skin rashes,
abdominal pain, and incontinence in children living close to the Love Canal site compared to controls
from other areas, as reported by the parents of the children. It has been noted in previous reviews (1,25)
that this study was conducted in 1980, 2 years after the residents of Love Canal had become aware of thehazardous waste problem, when media and public interest were high, and people were being evacuated.
This makes it likely that the results were biased by differential reporting of health problems. However, asimilar population of children (spending 75% or more of their childhood in the Love Canal area) had
significantly shorter stature for their age than control children after allowing for factors such as birthweight, socioeconomic status, and parental height (10). Vianna and Polan (11) found an excess of lowbirth weights (less than 2500 g) during the period of active dumping (1940-1953) in areas of Love Canal
where exposure had been highest. Rates of low birth weight between 1960 and 1978 after the site had
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

been closed were comparable to those in upstate New York as a whole. It is not clear whether exposure
from Love Canal was highest during the active dumping period or during the period after the site wasclosed, when the building of houses near the site increased and the landfill was leaking. A study byGoldman et al. (12) reported a 3-fold risk of low birth weight for children exposed during gestational life
to the Love Canal area compared to that for control children born elsewhere from 1965 to 1978. Data
were analyzed separately for homeowners and renters so that groups of similar socioeconomic status
were compared, and after allowing for confounding factors, the risk of low birth weight was significantly
increased for homeowners only. This finding is difficult to interpret because there are no strong reasons
to believe that homeowners would be more susceptible than renters to the effects of toxic chemicals. In
the same study an increased risk of birth defects was observed for both homeowners and renters.
Information on birth defects relied mainly on reports from parents. Some recall bias can therefore besuspected, in particular for defects of lesser severity, but this is unlikely to account for the entire
association found for major birth defects.
Berry and Bove (26) studied birth weight at the Lipari Landfill in New Jersey, a site for municipal andindustrial waste. Leachate from the site migrated into nearby streams and a lake adjacent to a residential
area. Inhalation of volatile chemicals emitted from the landfill and contaminated waters was thought tobe the most important exposure pathway. The site closed in 1971 after complaints of residents, but theheaviest pollution was estimated to have occurred during the late 1960s to the mid-1970s. The study
found a convincing increase in proportion of low birth weight babies (< 2500 g) and a lower averagebirth weight in the population living closest (within a radius of 1 km) to the landfill in the time period
when potential for exposure was thought to be greatest (1971-1975) compared to these factors in acontrol population. Although information on some confounding variables such as smoking, alcohol
consumption, and socioeconomic status was not available, mothers in the exposed area were more highly
educated and therefore appeared to be of higher socioeconomic status. One would expect higher birthweights in areas of higher socioeconomic status, so as the authors point out, confounding bysocioeconomic status does not explain the lower birth weights found. In time periods before and after
heavy dumping and off-site pollution, birth weights were higher in the area closer to the site than in thecontrol area, which supports the hypothesis that pollution from the waste site may have been related to
low birth weights in the community close to the site.
A range of reproductive effects including low birth weight was studied around the large BKK hazardous
waste disposal site in Los Angeles County, California (14), after previous investigations of vital records
found that trends in low birth weight and neonatal deaths corresponded closely with times and quantitiesof dumping at the landfill. Results for the whole study period showed no increase in adverse reproductive
effects, but during the period of heaviest dumping, birth weights were significantly lower in exposed
areas than in control areas using odor complaint frequency zones to classify exposure. All results were
adjusted for education, income, and race. The decrease in mean birth weight found in the high-odor
complaint zone was small (59 g) compared to that in the Lipari Landfill study (192 g) and was less than athird of birth-weight reductions caused by smoking during pregnancy (26). Odor complaint frequency
zones corresponded better with vinyl chloride monitoring data and meteorology around the site than did
census tract areas or distance-based (< 0.7 miles) exposure zones, and this was therefore thought to be
the most accurate method for classifying exposure. Using census tract or distance-based exposure zones,
smaller decreases in mean birth weight were found (35.2 g, p = 0.02 and 20.4 g, p = 0.25, respectively).
Miron Quarry, a large (the third largest in North America) municipal solid waste site in Montreal,
Quebec has prompted studies on both reproductive outcomes (low birth weight and preterm births) (27)http://ehpnet1.niehs.nih.gov/members/2000/suppl-1/101-112vrijheid/vrijheid-full.html (6 of 21) [5/31/2001 2:55:08 PM]

Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literatureand cancers (21). Gas from the site was the main environmental and health concern and a range of VOCs,
including a number of recognized or suspected human carcinogens, had been detected in the gas. An
excess of 20% in low birth weight was found among babies of mothers who were living in thehigh-exposure area adjacent to the landfill at the time of delivery, taking account of confounding factors
such as education and age of the mother. No excess was found in the low-exposure zone compared to acontrol area. Exposure zones were based on proximity to the site and accounted for the direction of
dominant winds. Control areas were selected that were similar to exposure areas on a number ofsociodemographic variables so as to limit the potential for confounding. The cancer study used the same
exposure zones and control areas and increases were found in incidences of cancers of the stomach, liver,prostate, and lung for men, and stomach and cervix/uterus for women. Incidences of cancers of otherorgan sites were not increased in the exposed areas. Age and sex were the only confounders that could becontrolled for directly and the authors admit that area matching for sociodemographic factors was basedon fairly broad zones. The landfill started operation in 1968 and cancer incidence was studied between
1981 and 1988, which allowed a maximum latency of only 20 years among those residents in the area
throughout the period.
In Mellery, Belgium, gases containing a complex mixture of VOCs escaped when the clay seal of alandfill site cracked. Because some of the detected chemicals were known mutagens and/or carcinogens,damage to chromosomes was studied and an increase in chromosome damage (sister chromatid
exchanges) was found among Mellery residents but not in unexposed subjects in subgroups of both
smokers and nonsmokers (15). In children 8-15 years of age, a more marked difference was foundbetween exposed and unexposed groups than among adults. The findings indicated exposures similar to
those of occupationally exposed populations. The adult unexposed comparison subjects were recruitedfrom a volunteer blood donor list and may therefore have comprised a group with risk behavior andexposure to possible risk factors for chromosome damage different from those of the general population.
They also reported less occupational exposure than the Mellery inhabitants. It is unclear how
occupational exposure was defined and results have not been adjusted for it. A follow-up study after site
remediation reduced the concentration of the atmospheric pollutants to background levels reported thatchromosomal damages in Mellery children had returned to background levels and were no longer
different from those for unexposed populations (28).
At the Drake Superfund Site, an industrial chemical dump in Pennsylvania, widespread on- and off-site
contamination of groundwater, soil, and surface water with organic (benzene, chlorinated benzene,
phthalates) and inorganic (arsenic, mercury) compounds prompted a cancer mortality and birth defects
study (29) and a community health survey (16). Air monitoring near the site identified a small number oforganic compounds, but the main exposure route was thought to be direct contact with surface waters andsoil in recreational areas near the site. Budnick et al. (29) found an increase in mortality from bladdercancer (cancer of primary a priori concern because of aromatic amines detected on and off site) in themale population of one of the counties surrounding the waste site compared to average mortality rates inthe entire state and the United States. Bladder cancer in females did not show such an effect. The authors
point out that an occupational effect for males working in the Drake chemical plant may explain the factthat the association was found in men only. No excess in risk of birth defects was found. The subsequent
health survey (16) found increased reporting of sleepiness and skin problems in the exposed communityand concluded that it was difficult to say whether toxic chemicals from the site, overreporting ofsymptoms by the exposed community (reporting bias), or other factors such as stress and occupational
exposure caused these symptoms.
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic LiteratureStudies of self-reported health symptoms. A number of other community health surveys haveinvestigated a wide range of health problems, including respiratory symptoms; irritation of skin, nose,and eyes; gastrointestinal problems; fatigue; headaches; psychological disorders; and allergies. Thesestudies have been conducted in response to concerns from the public, often triggered by smells and odors
from the sites. In a number of studies, self-reported health problems were increased in exposed
populations (people living close to the waste sites) compared to control populations [Drake Superfund
Site (16); Lowell, Massachusetts (17); Hamilton, Ontario (30); Stringfellow, California (31);
Queensland, Australia (32); McColl waste site, California (18); Houston, Texas (33); Harris County,
Texas (34)] (see Table 1 for details). The majority of these health surveys rely on residents reporting
symptoms and diseases through questionnaires or interviews. The possibility exists that higher reporting
rates of symptoms in exposed areas are at least partly explained by reporting and/or recall biases. From apublic health point of view, the findings of high symptom reporting, whether or not due to differential
self-reporting, may indicate the impact that stress and concerns related to landfill can have on ill healthand/or perceived ill health. In the survey by Ozonoff et al. (17), residents who indicated they were
worried about neighborhood pollution reported more symptoms than those who were not worried, both in
the exposed and the control area. Although this does not eliminate the possibility of an effect of toxic
chemicals from the site, it suggests that stress and/or recall bias may have been responsible for thefindings. Miller and McGeehin (34) and Dunne et al. (32) found increased symptom prevalence only inresidents who indicated they were worried about, or aware of, an environmental problem in theirneighborhood. The study by Lipscomb et al. (18) showed a 2-fold risk in most symptoms for residents
who were worried compared to those who were not worried among the exposed population. The authors
concluded that being worried, rather than a toxicologic effect from the site, explained the symptoms.
Hertzman et al. (30) used medical records to confirm certain symptoms and found no over- or
underreporting. They concluded that this finding indicated limited reporting bias; however, only a small
proportion of the respondents' records were reviewed. Moreover, seeing a physician (and therefore
having a medical record) may itself be related to concerns about the site. Baker et al. (31) studied
self-reported health problems as well as mortality, cancer incidence, and pregnancy outcomes frommedical registers at the Stringfellow waste dump in California. Self-reported diseases and symptoms
were the only outcomes that differed between exposed and unexposed areas. Again, a higher perceptionof threat was related to a higher risk of nearly all self-reported symptoms.
The complicated relation between worry, odor perception, and symptom reporting related to hazardous
waste landfill sites is further discussed by several authors (35-37).
Two recent studies around the French landfill of Montchanin used records of prescribed medication (19)and cases from general practitioners (GPs) (20) to define health outcome, in order to avoid biases related
to self-reporting of symptoms. Exposure classification in both studies was based on an individual index,
taking into account the concentration of airborne pollutants and daily activities of study subjects. Highconcentrations of VOCs were detected in areas near the site and both leachates and air from the site werereported to be highly toxic in 1988 and 1989, shortly after site closure. Consumption of drugs prescribedfor most conditions from 1987 to 1989 did not show a trend with exposure level, although a slight trend
was found for drugs taken for ear, nose, and throat, and pulmonary conditions. In the second study,
patients with conditions thought to be associated with dump emissions were compared to other GP
patients and an association was found for respiratory symptoms and psychological disorders. Again,
consulting a doctor for such conditions and subsequent diagnosis of the conditions by the physician may
be related to fears of adverse effects from the landfill rather than to toxic chemical effects.
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

Cluster Investigations. In addition to the above papers, a number of reports are available of geographicalcomparison studies initiated after high rates (clusters) of specific diseases were reported in the vicinity oflandfill sites. For example, increased rates of leukemia found in communities nearest a toxic waste dump
in North-Rhine Westfalia, Germany, supported a GP report of a cluster near the site (38). A cluster ofchildhood cancer reported by residents near a landfill site in Walsall, England, was not confirmed in ageographical comparison of rates in the ward containing the site to expected rates based on the regional
average (39). Only short reports of these two investigations have been published.Concerns from residents
and a GP about increased rates of congenital abnormalities (specifically gastroschisis, a defect in theabdominal body wall) among the population living near the Welsh landfill of Nant-y-Gwyddon were
supported by the finding that rates of congenital abnormalities in exposed wards were almost 1.9-foldthose in unexposed wards over the period from 1990 to 1996 (40). However, rates in the exposed wards
were already high (1.9-fold those of unexposed wards) between 1983 and 1987 before the site opened,
and it is unlikely, therefore, that these increased rates were due to the landfill. Four cases of confirmed
gastroschisis indicated a significant 9-fold excess in rates of gastroschisis among exposed wards between
1989 and 1996. A cluster of bladder cancer cases in one town in Illinois in the United States, wasobserved by researchers and subsequently linked to the presence of two contaminated wells close to alandfill site (41).
A general problem in the interpretation of all cluster investigations is that localized areas of high diseasedensity may occur even as part of a random pattern of disease. It is difficult to distinguish clusters
derived from this random pattern from those where there is a common underlying local cause (42,43).
Also, areas with higher disease densities, although part of the random pattern of disease, may be
selectively picked for study.
Studies of drinking water contamination incidents. The presence of chemicals in groundwater anddrinking water is an important factor in determining the risk posed by landfill sites. However, it does nottell us what effect, if any, the consumption of contaminated water has on human health. Studies ofadverse health effects prompted by the contamination of well water used for drinking water and otherdomestic uses by hazardous substances from waste disposal sites (mainly sites where chemical waste
drums were buried) are discussed below. Literature on contaminated water and potential health effects ismore extensive than that presented in this section, which focuses only on water contamination directly
related to the disposal of waste. The 1991 review by the National Research Council (2) gives a morecomprehensive review of studies on contamination of domestic water supplies and health effects andconcludes that although the available literature is scanty and not conclusive, drinking watercontamination could lead to adverse health effects. Most of the studies summarized below have been
discussed extensively in previous reviews (1,2).
In Woburn, Massachusetts, toxic chemicals (industrial solvents, mainly trichloroethylene) from a waste
disposal site were detected in municipal drinking water wells. Residents of Woburn reported a cluster of
12 leukemia cases in children, and a first study confirmed that this number was significantly higher than
expected on the basis of national rates (44). The problems with cluster analyses are discussed above.
Because of lack of information on exposure to the contaminated wells, it was not possible in this firstreport to link the leukemia cases with exposure to the well water. Lagakos et al. (45) followed up thesefindings by compiling an exposure score for residential zones in Woburn using information on whatfraction of the water supply in each zone had come from the contaminated wells annually since the startof the wells. Childhood leukemia incidence, perinatal deaths, congenital anomalies, and childhood
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literaturedisorders were studied in relation to the exposure scores. A significant excess was found again
comparing leukemia rates for Woburn with national rates, and an association was found between
leukemia incidence and exposure scores. The pregnancy outcome survey found associations with eye/ear
congenital anomalies and central nervous system/oral cleft/chromosomal anomalies (mostly Down
syndrome) but not with low birth weight or most childhood disorders. Pregnancy outcomes wereself-reported in this study, but because residents were not aware of their exact exposure scores, theauthors conclude that it is unlikely that this led to substantial differential overreporting. Byers et al. (46)undertook a study of 28 family members of patients with leukemia in Woburn. Damage to the immune
and nervous systems was found in exposed relatives but not in unexposed controls. Exposure in thisstudy was not measured by exposure to contaminated well water but by being related to a leukemia
patient in Woburn, which makes it difficult to interpret the findings. The authors point out that it is
impossible to say whether the association is due to an inherited predisposition or to a common
environmental exposure of family members to agents that damage the immune system.
A number of studies followed the contamination of two drinking-water wells in Santa Clara County,
California, with chlorinated solvents that had leaked from an underground waste storage tank. Residents
living near one of the contaminated wells reported a cluster of adverse pregnancy outcomes, mainly
spontaneous abortions and congenital heart defects. A first investigation (47) confirmed a significant
excess of cardiac anomalies in the service area of the water company that operated the contaminated wellcompared to those among residents of an unexposed area. The excess was found within the potentially
exposed time period and not in an unexposed time period after the well was closed. The authors conclude
that the solvent leak was an unlikely explanation for the excess of cardiac anomalies found because theexcess occurred mainly in the first 12 months of the exposed time period, and there was a significant (p =0.03) deficit of cases during the second 8 months corresponding to the time when exposure was thought
to be more certain. However, it is unclear when the leak started and the potentially exposed period was
defined beforehand as the full 20-month period. A second study in the same area reported an increased
risk of all congenital malformations combined and spontaneous abortions (48). A follow-up study
including a second exposed area did not observe an increase in either outcome in this second area, eventhough it was thought to have the same water exposure as the original area (49). An exposure study
estimating monthly concentrations of solvents in each census tract found no difference in probability of
exposure between women with adverse pregnancy outcomes and women with normal births (50).
Subsequent studies investigating water consumption in Santa Clara County report significant associations
between reported tap water consumption and risk of cardiac defects (51) and spontaneous abortions(52,53), regardless of whether women lived in areas that received contaminated water. As the authors ofthese studies point out, recall biases cannot be excluded.
In Hardeman County, Tennessee, well water used as drinking water by residents was found to becontaminated with high concentrations of carbon tetrachloride and other chlorinated compounds after
complaints were received about the taste of the water. A nearby landfill where 300,000 barrels of
pesticide waste had been buried was responsible for the contamination. Analysis of indoor air andbathroom air while showers were running both indicated detectable levels of carbon tetrachloride andother organic compounds in houses that received water from the contaminated wells. Carbon
tetrachloride has been identified in toxicologic studies as a strong liver toxin. The investigation,
conducted several months after the population had stopped using the water for drinking, showedabnormally high levels of liver enzymes (indicating liver damage) in residents who had used
contaminated water compared to controls, who had not (13). The authors concluded that these high liver
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

enzyme levels probably resulted mainly from exposure due to washing and toilet water uses, and possibly
from previous exposure through drinking and cooking. Two months later, when use of the well had
completely stopped, liver function in the exposed population had returned to normal. This study
benefited from relatively well-documented exposure information and a clear hypothesis about thepossible health effects (i.e., liver disease) related to exposure to carbon tetrachloride.
Leakage from an industrial dump of chemical waste drums in New Jersey caused contamination ofgroundwater and well water with organic chemicals (including benzene, toluene, trichloroethylene, andlead). Najem et al. (54) found higher self-reported prevalence of respiratory disease and seizures but notcancer, liver illness, and skin disease in people living in a high-exposure area estimated on the basis ofgroundwater flow patterns. Residents in the high-exposure area used private drinking-water wells, ate
home-grown food, and smoked more often than populations living in unexposed areas, and when thesefactors were adjusted for, differences in health outcomes disappeared. Adjusting for possible exposure
routes such as local food consumption and use of private wells may have led to overadjustment, however,which would explain why no differences in health outcome were found.
An ex-military base in Dauphin County, Pennsylvania contained drums of toxic chemicals, fly ash, andother waste; well water for homes located on the perimeter of the site was contaminated withtrichloroethylene, PCBs, pesticides, and other chemicals (55). Residents were instructed to stop using thewater. Higher rates of eye irritation, diarrhea, and sleepiness were reported by residents of householdswith contaminated well water than by residents of households not having contaminated water.
Multisite Studies
The problems with single-site studies prompted by community pressures have increasingly beenrecognized, and recently several large studies have investigated adverse health effects near sets ofhundreds of sites selected independently of community concerns or reported disease clusters (Table 2).
These studies have the additional advantage of large numbers of subjects, which would give them enoughstatistical power to detect small increases in risk of rare diseases such as birth defects and specificcancers. On the other hand, their large scale makes exposure assessment even more complicated than insingle-site studies, as adequate information must be collected for each of many sites. A number of thestudies discussed below have used the U.S. National Priority Listing (NPL) of hazardous waste sites
developed by the U.S. Environmental Protection Agency (U.S. EPA) to select their sites. The NPL ranks
all hazardous waste sites in the United States deemed to be of considerable threat to the environment or
public health. NPL sites have been relatively well assessed with respect to the potential or actual
migration of hazardous chemical substances from the sites through groundwater, surface water, and air(2). Most multisite studies, however, were not able to distinguish between different types and pathwaysof contamination and, in absence of better exposure data, based their assessments of exposure on distanceof residence from the sites or residence in an area with a site. Exposure misclassification, if
nondifferential, may be expected to dilute true effects in these investigations. Multisite studies mainly
investigated cancers and reproductive outcomes.
Cancer studies. Griffith et al. (56) identified 593 NPL sites over the entire United States wherecontamination of groundwater used for drinking water had been detected by laboratory analyses. Cancer
mortality rates for counties containing one or more of these NPL sites were compared to those forcounties not containing sites and raised levels of lung, bladder, stomach, and rectum cancer were found.
These results were not adjusted for confounding factors such as socioeconomic status and smoking andare therefore difficult to interpret.
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

A case-control study in New York State (57) examined lung-cancer in relation to residence in a census
tract with a waste site. Twelve waste sites known to contain suspected lung carcinogens were studied. A
questionnaire survey among next of kin of the deceased cases and controls attempted to collectinformation on factors such as smoking, diet, education, and residential history. Smoking was
significantly more frequent among cases, but there was no association between having lived in or
duration of living in an exposed census tract and risk of lung cancer. Low response rates (around 60%)
and possible recall bias limit this study.
A recent study in New York State (58) investigated cancer risks near 38 landfills where migration oflandfill gas through soil was likely. Migration of soil gas could result in indoor exposure in nearby
houses to hazardous VOCs carried with the landfill gas. Potential exposure areas were defined aroundeach site, and extended 250 ft from the landfill at 36 sites and 500 ft at 2 sites. Incident cases of cancer
collected from the New York State Cancer Registry were compared with a random selection of deaths
from causes other than cancer, matched by age and sex. Only cancers of the liver, lung, bladder, kidney,
and brain, and non-Hodgkin lymphoma and leukemia were studied, as they were regarded potentiallysensitive to chemical exposures. Statistically significant excesses in the defined exposure areas werereported only for bladder cancer in women and leukemia in women. The results were adjusted forsociodemographic characteristics of the areas of residence. No information was available on individual
factors such as smoking or on how long cases and controls had been living at certain addresses. The useof deceased controls makes interpretation of this study extremely complicated. The deceased populationfrom which controls were selected may differ from the population from which the cases were drawn on anumber of variables, including their residence locations.
Studies of reproductive outcomes. Shaw et al. (59) conducted a study on the risk of congenital
malformations and low birth weight in areas with landfills, chemical dump sites, industrial sites, andhazardous treatment and storage facilities in the San Francisco Bay, California area. Census tracts wereclassified as a) no hazardous site in area, b) hazardous site in area but no evidence of human exposure,and c) hazardous site and plume in the area with evidence of potential human exposure. A small increase(1.5-fold) in risk was found for heart and circulatory malformations in the areas with potential human
exposure. This increased risk was present across chemical classes and exposure routes. Risk of othermalformations or low birth weight was not significantly increased. Results were adjusted for somepotential risk factors (maternal age, race, sex of child, birth order) but not for socioeconomic status.
Reproductive outcomes have been studied in a number of other multisite studies. Sosniak et al. (60)
investigated the risk of adverse pregnancy outcomes for people living within 1 mile of a total of 1,281
NPL sites over the entire United States. The risk for low birth weight and other pregnancy outcomes(infant and fetal death, prematurity, and congenital anomaly) was not associated with living near a site
after taking into account a large number of potential confounding factors, including socioeconomic
variables collected through questionnaires. However, only around 63% of women originally sampled forthe study returned the questionnaire and were included in the study. Also, it is unclear how congenital
anomalies were defined, and no subgroups of malformations were studied.
Geschwind et al. (61) investigated the risk of congenital malformations in the vicinity of 590 hazardous
waste sites in New York State. A 12% increase in congenital malformations was found for people living
within 1 mile of a site. For malformations of the nervous system, musculoskeletal system, andintegument (skin, hair, and nails), higher risks were found. Some associations between specificmalformation types and types of waste were evaluated and found to be significant. A dose-response
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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

relationship (higher risks with higher exposure) was reported between estimated hazard potential of thesite and risk of malformation, adding support to a possible causal relationship. However, a follow-up
study of Geschwind's findings (62) found no relation between two selected types of malformations(central nervous system and musculoskeletal) and living near a hazardous waste disposal site. The study
did report an increased risk of central nervous system defects for those living near solvent- or
metal-emitting industrial facilities. Subjects for the first 2 years of this study were also included inGeschwind's study, and 2 more years were studied. Marshall et al. (62) attempted to improve theexposure measurement in the first study by assessing the probability of specific contaminant-pathway
combinations in 25 sectors of the 1-mile exposure zones (63). The risk of particular pathways orcontaminant groups could not be investigated, however, because of limited numbers of cases in eachsubgroup. Hall et al. (64) used the same method of exposure assessment to study renal disease near 317
waste sites in 20 counties in New York State. Increased risks were found for associations between renal
disease and residential proximity to a site (within 1 mile), the number of years lived near a site, and a
medium or high probability of exposure, although the associations did not reach statistical significance.
A study by Croen et al. (65) based exposure measurement on both residence in a census tract containing
a waste site and distance of residence from a site. Three specific types of birth defects (neural tube
defects [NTDs], heart defects, and oral clefts) were studied; little or no increase in the risk was foundusing either measure of exposure. Risks of neural tube (2-fold) and heart defects (4-fold) were increased
for maternal residence within 1/4 mile of a site, although numbers of cases and controls were too small(between 2 and 8) for these risk estimates to reach statistical significance. Births were ascertained from
nonmilitary-base hospitals only, and the authors point out that the increased risk of NTDs may haveresulted from lower ascertainment of exposed controls than exposed cases where exposure zones
included military bases. Military base residents with pregnancies affected by NTDs may have been more
likely to deliver in nonmilitary hospitals than residents with unaffected pregnancies.
A first European multisite study recently reported a 33% increase in all nonchromosomal birth defects
combined for residents living within 3 km of 21 hazardous waste sites in 10 European regions (66).
Neural tube defects and specific heart defects showed statistically significant increases in risk.
Confounding factors such as maternal age and socioeconomic status did not readily explain the results.
The study included both open and closed sites that ranged from uncontrolled dumps to relatively modern
controlled operations. This disparity makes it difficult at this stage to conclude, if indeed the association
is causal, whether risks are related to landfill sites in general or whether specific types of sites may beposing the risks.

Conclusions
The presence of large quantities of mixtures of potentially hazardous chemicals in landfill sites close toresidential populations has increasingly caused concern. Concerns have led to a substantial number ofstudies on the health effects associated with landfill sites. From this review we can conclude that
increases in risk of adverse health effects have been reported near individual landfill sites and in somemultisite studies. Although biases and confounding factors cannot be excluded as explanations for thesefindings, the findings may indicate real risks associated with residence near certain landfill sites.
For several reasons, evidence is limited for a causal role of landfill exposures in the health outcomes
examined despite the large number of studies. Effects of low-level environmental exposure in the general

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Health Effects of Residence Near Hazardous Waste Landfill Sites: A Review of Epidemiologic Literature

population are by their nature difficult to establish. Also, existing epidemiologic studies are affected by arange of methodologic problems, potential biases, and confounding factors, making the interpretation ofboth positive (statistically significant increase in risk) and negative (no increase in risk) findings difficult(67). Lack of direct exposure measurement and resulting misclassification of exposure affects moststudies and can limit their powers to detect health risks.
It is possible that studies not showing associations have been less likely to be included in this review
because they may have been less likely to be submitted or selected for publication, thereby causing thereview to be biased toward studies that did report positive associations. However, a number of so-called
negative studies have been published and included in this review. We feel that most large, good-quality,
epidemiologic investigations, particularly those starting with an a priori hypothesis rather than a specificcluster, would have resulted in publication, whether or not the findings were positive.
An increase in self-reported health outcomes and symptoms such as headaches, sleepiness, respiratory
symptoms, psychological conditions, and gastrointestinal problems has been found consistently in healthsurveys around sites where local concerns were evident (9,16-18,30-34,54,55). In these health surveys
symptoms were usually reported by the exposed population without further confirmation of the diagnoses
by medical examination. It is not possible at this stage to conclude whether the symptoms are an effect of
direct toxicologic action of chemicals present in waste sites, an effect of stress and fears related to thewaste site, or an effect of reporting bias (the tendency of exposed people to remember and report more
symptoms than unexposed people). Several authors have discussed the possibility that odor complaints
and related worry about a site may trigger symptoms of stress-related disease or lead to an increased
awareness of existing symptoms (36,37). Further research in this area is urgently needed to improve ourunderstanding of the impact of social factors and risk perceptions on both actual and perceived ill healthin waste site communities. Issues of environmental equity and environmental justice must form an
integral part of such research.
Evidence for a causal relationship between landfill exposures and cancers is still weak. Cancers are
difficult to study because of long latency periods, as discussed in previous sections. Also, cancer studies
have mainly compared incidence or mortality rates between geographic areas without collecting adequate
information on confounding factors. Excesses in bladder, lung, and stomach cancer and leukemia werereported in more than one study (21,29,41,45,56,58). Well-designed studies with long follow-up andgood quality information about confounding factors such as smoking are needed to confirm thesefindings.
A number of studies have suggested a relationship between residential proximity to landfill sites andadverse pregnancy outcomes. An increase in infants with low birth weights has been the most consistentfinding in single-site studies (11,12,14,26,27). These were generally well-designed studies and low birthweight is thought to be a sensitive marker of effects of chemical exposures. Small increases in the risk ofbirth defects and certain specific birth defects (cardiac defects, central nervous system defects,
musculoskeletal defects) have been reported, mainly in multisite studies (12,59,61,65,66). Studies arestill too few, however, to draw conclusions regarding causality. Fetuses, infants, and children are
generally thought to be more vulnerable and therefore experience toxic effects at lower doses than theadult population (25). The finding of shorter stature in Love Canal children (10) may also be an exampleof this.
An increased presence of chromosomal changes was reported in the vicinity of a landfill site in Mellery,

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Belgium (15,28), but not in Love Canal (8). Findings in Mellery were related to children in particular,
which may again be an indication that children are more susceptible to low-level exposures from waste
sites. It is not clear at present how well chromosomal changes predict cancer risk in humans.
Other adverse health outcomes such as abnormalities in liver function (13) and in renal disease (64) havealso been reported in relation to hazardous waste exposure, although in single studies only.
For the future planning and regulation of landfill sites it is important to know which types of sites aremost likely to entail risks. Landfill sites may differ enormously in the conditions that render themhazardous, and conditions that determine the exposure to and resulting health risks posed by any waste
site are likely to be unique to that particular site. Such conditions may include the types, quantities, andage of the waste present; hydrogeologic and metereologic factors; and site management and engineering
practices. We have not in this review attempted to relate technical aspects of waste disposal to healtheffects. Much of the existing epidemiologic work investigates large, old sites, uncontrolled dumps, andsites where heavy off-site migration of chemicals was detected. On the basis of current evidence, wecannot extrapolate findings for these individual sites to landfill sites in general or conclude which landfill
sites are more likely than others to affect the health of nearby human populations.
It is also not possible to determine whether sites with airborne or waterborne exposures are more likely topose a risk to human health. Although drinking water contamination is usually the primary concern
related to landfill sites, in most cases local water supplies do not originate from the local area. Most
studies, therefore, concern landfill sites where no local drinking-water wells were present and potential
exposure was either airborne or through other routes such as direct contact and consumption ofhome-grown vegetables.
At present information regarding adverse health effects of exposure to landfill sites in European countries
is largely lacking.

Further Research Needs
Research into the health effects of landfill sites is relatively immature, and further research could
improve our current understanding (1,2,25,68). Future studies of landfill sites would greatly benefit froma more interdisciplinary approach, drawing from the fields of landfill engineering, environmental
sciences, toxicology, and epidemiology.
Improvements in the base of toxicologic and epidemiologic data on effects of specific chemical
exposures would improve our understanding of possible risks of the migration of these chemicals fromlandfill sites into the environment. Johnson and DeRosa (69), in a recent review of toxicologic hazards ofSuperfund waste sites, conclude that although a large body of toxicologic research is under way to assess
the toxicity of chemicals commonly contaminating the environment surrounding waste sites, equallysignificant work is still to be done before these chemicals have adequate toxicity profiles that can be usedby health and risk assessors. Johnson and DeRosa discuss data needs established by the Agency for
Toxic Substances and Disease Registry and the U.S. EPA for research of individual chemicals and findthese needs mainly in dose-response studies, reproductive studies, and immunotoxicology studies.
Improved data on effects of individual chemical exposures would improve the quality of quantitative risk
assessments that can be made for landfill exposures. However, quantitative risk assessments are based toa large extent on unverifiable assumptions, and therefore cannot negate the necessity for direct

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epidemiologic studies of people living near landfill sites.
More research into effects of chemical mixtures and possible interactions between single chemicals isneeded to improve understanding of effects of multiple chemical exposures. Such research is complex,
but new research initiatives are under way, mainly in the United States. For example, the U.S. EPAMIXTOX database, which contains toxicologic data on interactions of hundreds of pairs of chemicals, isa promising new development (70). Research developments and future directions in this field are
discussed in detail by a number of authors (70-72).
The investigation of single landfill sites is important as a response to community concerns. Moremultisite studies with large study populations should also be conducted to draw conclusions about moregeneral risks. Ideally, such multisite studies should attempt to classify sites in such a way that risks
related to specific site characteristics can be investigated. However, systematic site assessments needed
to underpin such classifications are at present totally lacking in Europe. There is little detailed
information on waste inputs, especially for old landfills, and monitoring practices vary hugely for factors
such as frequency of monitoring, the environmental media monitored, and types of chemicals monitored.
Standardized waste-input recording systems and monitoring practices across European countries and theavailability of summary reports of waste inputs and monitoring results would aid site classifications for
epidemiologic studies as well as risk assessments. A recent report evaluating the use of a risk assessment
tool on two U.S. and three U.K. landfill sites concluded that in the United Kingdom it is not possible tocharacterize the majority of landfills, even to the level at which a simple risk assessment framework canbe employed on a site-specific basis. This particularly applies to the characterization of emplaced waste(73).
Epidemiology has increasingly made use of so-called biomarkers--biological monitors of either theinternal dose of a chemical (biomarkers of exposure) or the biologic response to exposure (biomarkers ofearly effect). Biomarkers of the first type measure levels of chemicals in human tissue and fluids (e.g.,
blood, urine). These techniques can generally measure only a small number of chemicals, and their use islimited to situations in which environmental monitoring data indicate specific landfill chemicals that areof particular concern. The presence of chemicals in the body is currently difficult and costly to measure,but this may change. Biomarkers of the second type measure biological responses such as chromosomalchanges (sister chromatid exchanges) and molecular changes (DNA adducts), and could be seen as early
effect manifestations. Interpretation of these effect biomarkers is difficult; their link with clinically overt
disease remains unclear, but their use could give studies much greater statistical power than studies ofrare disease outcomes. Biomarker techniques have been used mainly in occupational settings and there
has been less discussion of their use in environmental studies (74,75). Collaboration is required between
epidemiologists and basic scientists to further develop biomarker techniques for use in studies ofenvironmental exposures.
Specific areas of further research likely to prove most useful are● The study of vulnerable groups--groups of the population likely to develop adverse health effects
at levels of exposure lower than those of the general population. Such groups include: fetuses,
infants, and children; elderly people; and people with impaired health.
● The study of people with higher exposures, for example, children (because they come into higher
contact with potentially contaminated soil); people who eat local food products; workers at waste
sites; people with life-styles (possibly socioeconomically determined) that lead to higher

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exposures.
● The study of worst-case landfills. In the absence of adequate exposure data, it is difficult to define
worst-case sites. Ranking systems are in use, e.g., in the Superfund program (76), to rank waste
sites according to their hazard potential, but their application generally requires extensive site
investigations. Few epidemiologic studies would have the resources to carry out suchinvestigations. It could be argued that identification of worst-case landfills should form part ofregulatory practice in Europe. However, in the absence of systematic investigation of this kind, thestudy of sites where high off-site contamination has been detected and sites that have been subject
to less regulation (possibly sites in developing countries or Eastern Europe) could be suitable forthe study of worst-case scenarios provided appropriate health data can be collected.
It is possible with suitable investment to improve levels of understanding about risks of hazardous wastes
to human health. However, because of the complicated nature of the exposure, it is likely that there will
always remain a degree of uncertainty regarding health effects of landfill sites.
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