Abstract:
This study is comprised of three projects designed to characterize the fate and
transport of S-triazine herbicides (e.g., atrazine), chloroacetanilide herbicides (e.g.,
metolachlor) and the transformation products (TPs) of those herbicides in surface waters
of the Potomac River watershed in Virginia. The projects include instrumental-method
development, field-method development and long-term implementation of those methods
in a twelve month study on the North Fork of the Shenandoah River.
The goal of project 1 was to develop a robust method of analyzing surface water
samples for the target analytes using solid-phase extraction (SPE) cartridges and a single
quadrupole LC-MS system. Estimated method detection limits averaged 0.3 ± 0.1 ng L-1.
Spike recoveries ranged from 94.2% ± 4.8% for S-triazines and their TPs and 95.9% ±
19% for chloroacetanilides and their TPs, thus qualifying the method for instrumental
analysis.
The goal of project 2 was to develop field sampling protocols by examining the
temporal changes in the seasonally applied herbicides over a seven month period and
relating those changes to spatial variables in the upper Shenandoah River basin and in
Cedar Run, both tributaries to the Potomac River. TP concentrations increased rapidly
following the application period. Substantial differences in TP to atrazine ratios
distinguished the Shenandoah River from the Cedar Run basin. Principal component
analysis showed that concentration did not correlate well with river flow (discharge).
The goal of the third project was to characterize the major biogeochemical
processes in a river system located in the western section of Virginia. Surface water
samples were obtained during 14 sampling trips over a 12 month period beginning on 29
March 2008 and culminating on 28 February 2009 from 4 sites along the North Fork of
the Shenandoah River in Virginia. Detection frequencies were 100% for five of the
target analytes. The desethylatrazine to atrazine concentration ratio (DAR) increased
linearly over the study period with a value of ~0.4 at the spring flush period to ~2.5 at the
end of the study. Transformation rates for S-triazines ranged from 0.025 to 0.031 day-1.
The removal rates for total herbicide concentrations ranged from 0.019 to 0.050 day-1.
Steady-state concentrations for 3 of the 4 sites were above 100 ng L-1.
The instrumental and field methods developed in this study proved effective and a
long term study using those methods successfully characterized the primary processes
affecting the fate and transport of these herbicides in an important surface water system.
