Authors
Xiaomei Ma, Patricia A. Buffler, Robert B. Gunier, Gary Dahl, Martyn
T. Smith, Kyndaron Reinier, and Peggy Reynolds.
Title
Critical windows of exposure to household pesticides and the risk of
childhood leukemia
Journal
Environmental Health Perspective. 110: 955-960. 2002.
Summary
The goal of Northern California Childhood Leukemia Study (NCCLS) is
to explore the etiological role of household pesticide exposure and
risk of childhood leukemia. Although the relationship between household
pesticide exposure and childhood leukemia has been examined in numerous
studies the results have been inconclusive or inconsistent, making it
difficult to clarify the role of pesticides in the etiology of this
cancer. The inconsistencies of these previous studies have been due
to limitations including small numbers of cases, study design, problem
in recall and reporting of household pesticide exposure, matching criteria,
method and timing of data collecting, definition of exposure, enlistment
control, and the use of alternate respondents. The NCCLS was designed
to collect data collection on household pesticide exposure using in-home
personal interviews.
This study used
a total of 162 newly diagnosed leukemia patients during 1995-1999 and
162 matched controls which were randomly selected from the birth registry.
In the NCCLS each pesticide was classified according to the name and
the purpose of use, frequency of use, and the time of use (3 months
before pregnancy, pregnancy, years 1, 2, and 3 after birth). Pesticides
and insecticides were categorized according to professional services
or individual uses, indoor, and outdoor use. The insecticide exposure
include professional pest control services, use of different products
to control ants, flies, cockroaches, spider, termites, and plant/tree
insects. Herbicide exposures consisted of professional lawn and weed
control services, flea collars, indoor fogger, and flea control products.
The results of this
study suggest that the use of professional pest control services is
associated with an increased risk of leukemia, when exposures occur
at any time from one year before birth to three years after (OR= 2.8
and 95% confidence interval 1.4-5.7). The indoor pesticide exposure
was associated with an elevated risk of childhood leukemia while no
significant association was observed with outdoor pesticide exposure.
There was no association between use of flea control products and the
risk of leukemia.
The authors of the
study demonstrated that the exposure to insecticide and risk of leukemia
varied with the highest risk observed for exposure during pregnancy
(OR= 2.1; 95% CI, 1.1-4.3) and lowest during year 3 (OR= 1.2; 95% CI,
0.7-2.2). Exposure to insecticide significantly increased the risk of
leukemia during the 4 year period (from 1yr before birth to age 3) this
study (OR= 2.2; 95% CI, 1.1-4.3) examined. Also more frequent exposures
to insecticides were associated with a higher risk of leukemia. However,
leukemia risk following exposure to insecticide during pregnancy was
higher than exposure after birth, suggesting that the fetus is potentially
more sensitive to carcinogens in the insecticides used. It has been
hypothesized that some chromosome translocation events related to childhood
leukemia have a prenatal or even a preconceptual origin.
Overall, the design
of this case-control study was to reduce the general biases in epidemiological
studies by exposure classification error and distinguishing between
the risks associated with different types of pest control, and identifies
the importance of the timing and location of exposure. The NCCLS is
one of the first studies that addresses critical window of exposure,
that is, the timing of household pesticide exposures. However, a limitation
in this study can be related to use of broad subgroups of pesticides
whereas no specific chemical was measured. Also, the small sample size
used in this study reduces the confidence in the study results. Regardless,
this study does bring to light an import point in the endocrine disruption
and cancer field. Specifically, in vitro and animal tests for carcinogenicity
of the active ingredients in these pesticides tend to yield negative
results and suggest that these agents will not be carcinogenic in humans.
If confirmed in future research, the results of the present study would
suggest several potential problems such as: (1) current testing strategies
are not sensitive enough to detect compounds that will be carcinogenic
in humans; (2) there are ingredients present in the commercial mixture
that are carcinogenic and have not been evaluated; or (3) that chemicals
present in the commercial pesticide mixture interact to induce cancers.
It may therefore be necessary to study commercial pesticide preparations
for their potential to cause cancer in animals as a first step in unraveling
this paradox.