For centuries, several hundred pesticides have been used to control in
sects. These pesticides differ greatly in their mode of action, uptake
by the body, metabolism, elimination from the body, and toxicity to h
umans. Potential exposure from the environment can be estimated by env
ironmental monitoring. Actual exposure (uptake) is measured by the bio
logical monitoring of human tissues and body fluids. Biomarkers are us
ed to detect the effects of pesticides before adverse clinical health
effects occur. Pesticides and their metabolites are measured in biolog
ical samples, serum, fat, urine, blood, or breast milk by the usual an
alytical techniques. Biochemical responses to environmental chemicals
provide a measure of toxic effect. A widely used biochemical biomarker
, cholinesterase depression, measures exposure to organophosphorus ins
ecticides. Techniques that measure DNA damage (e.g., detection of DNA
adducts) provide a powerful tool in measuring environmental effects. A
dducts to hemoglobin have been detected with several pesticides. Deter
mination of chromosomal aberration rates in cultured lymphocytes is an
established method of monitoring populations occupationally or enviro
nmentally exposed to known or suspected mutagenic-carcinogenic agents.
There are several studies on the cytogenetic effects of work with pes
ticide formulations. The majority of these studies report increases in
the frequency of chromosomal aberrations and/or sister chromatid exch
anges among the exposed workers. Biomarkers will have a major impact o
n the study of environmental risk factors. The basic aim of scientists
exploring these issues is to determine the nature and consequences of
genetic change or variation, with the ultimate purpose of predicting
or preventing disease.