Over
the past four decades, numerous studies have established that pesticides, which
typically are applied at the land surface, can move downward through the
unsaturated zone to reach the water table at detectable concentrations. The
downward movement of pesticide degradation products, formed in situ, also can
contribute to the contamination of ground water. Once in ground water,
pesticides and their degradation products can persist for years, depending upon
the chemical structure of the compounds and the environmental conditions.
Scientists
at the U.S. Geological Survey (USGS) investigated the occurrence of selected
pesticides and their degradation products in ground water during a study funded
by the USGS National Water-Quality Assessment (NAWQA) Program. Specifically, the
authors examined several of the factors that can influence the likelihood with
which pesticides and their degradation products are detected in shallow ground
water – including oxidation-reduction (redox) conditions and ground-water
residence times – at four study sites across the United States. Results from the study
were published in the May-June 2008 issue of the Journal of Environmental
Quality.
The
study revealed that the pesticides and degradation products detected most
frequently in shallow ground-water samples from all four areas were
predominantly from two classes of herbicides—triazines and chloroacetanilides.
None of the insecticides or fungicides examined were detected in ground-water
samples. In most samples, the concentrations of the pesticide degradation
products greatly exceeded those of their parent compounds. Pesticides or their
degradation products were detected most commonly in ground water that recharged
between 1949 and 2004, and in monitoring wells spanning the full depth range
(about 2 to 52 m) examined—from the shallowest to the deepest wells—in all four
study areas. Comparisons of pesticide concentrations with a variety of
environmental variables indicated that redox conditions, ground-water residence
times, and the concentrations of dissolved oxygen and excess nitrogen gas from
denitrification (the breaking down of nitrogen compounds, such as nitrate) were
all important factors affecting the concentrations of pesticides and their
degradation products in all four ground-water systems.
The
four sites selected for this study were located in agricultural
landscapes in Maryland, Nebraska, California and Washington. They also
were selected
for variability in overall land use, crops grown, climate, agricultural
practices, irrigation, geohydrologic settings and redox conditions.
During the
spring of 2004, water samples were collected from a network of 59
shallow
single or clustered monitoring wells, and analyzed for the occurrence
of 45
pesticides and 40 pesticide degradation products, including herbicide,
insecticides and fungicides.
Greg Steele, senior
author for this study, states, “Atrazine and its degradation product
deethylatrazine both persisted in similar amounts at the Nebraska site, but in water samples
from the other three study sites, there was little change with apparent age of
water as the fraction as deethylatrazine generally exceeded 80 percent of the
sum of atrazine and deethylatrazine. On the other hand, in three of the four
areas studied (Washington excluded because it did not
have any detections of metolachlor or its degradation products), the proportion
of metolachlor in ground water was far less than that for its degradation
products.”