The effect of no-tillage practices on water quality exiting the root z
one of deep, well-drained fields is largely unknown. This project was
initiated to determine herbicide leaching characteristics as influence
d by tillage practice and herbicide formulation. The research site con
sisted of four adjacent (0.25-ha) fields, two fields each dedicated to
either tilled or no-tillage management. One field in each tillage reg
ime received a controlled-release formulation of atrazine thyl-N'-(1-m
ethylethyl)-1,3,5-triazine-2,4-diamine and alachlor [2-chloro-N-(2,6-d
iethylphenyl)-N- (methoxymethyl)-acetamide, starch encapsulated], whil
e the others received standard herbicide formulations of atrazine and
alachlor. Both herbicide formulations were annually applied at the sam
e rate: 1.7 kg ha(-1) for atrazine and 2.8 kg ha(-1) for alachlor. Atr
azine, deethylatrazine [DEAT; 6-chloro-N-(1-methylethyl)-1,3 ,5-triazi
ne-2,4-diamine), alachlor, and Br- concentrations were monitored with
12 suction lysimeters (six each at 1.5 and 1.8-m depths) in each field
. Alachlor was detected in <3% of all samples collected, regardless of
tillage practice or herbicide formulation, while atrazine was detecte
d in >41% of the samples. Under no-tillage, atrazine was detected in <
28% of the samples with <13% exceeding the U.S. Environmental Protecti
on Agency Health Advisory level of 3 mu g L(-1) atrazine. Under tilled
conditions, 53% of the samples contained atrazine, with 35% exceeding
3 mu g L(-1) atrazine. Averaged atrazine metabolite concentration of
DEAT under no-tillage was 0.52 mu g L(-1) vs. 0.39 mu g L(-1) for till
ed fields. Similar Br- transport between tillage practices and reduced
atrazine levels under no-tillage fields suggest that no-tillage manag
ement, on deep well-drained soils, can have a positive impact on groun
dwater quality.