Rf. Spalding et al., STUDY OF PESTICIDE OCCURRENCE IN 2 CLOSELY SPACED LAKES IN NORTHEASTERN NEBRASKA, Journal of environmental quality, 23(3), 1994, pp. 571-578
Dissolved pesticide concentrations in 168 water samples collected from
two closely-spaced lakes between early May 1990 and mid-june 1991 ind
icated large differences in impacts from watershed nonpoint source inp
uts. Pesticide levels in Maskenthine Lake, a small impoundment of 34 h
a, increased in response to spring and early summer runoff events. Twe
lve pesticides [atrazine, 2-chloro-4-ethylamino-6-isopropylamino-s-tri
azine; alachlor, ro-N-(2,6-ethylphenyl)-N-(methoxymethyl)acetamide; me
tolachlor, -ethyl-6-methylphenyl)-N-(2-methoxy-1-methylethyl) acetamid
e; cyanazine, 2-[[4-chloro-6-(ethylamino)s-triazin-2-yl] amino]-2-meth
ylpropionitrile; EPTC, S-ethyl dipropylthiocarbamate; butylate, S-ethy
l diisobutylthiocarbamate; propachlor, 2-chloro-N-(1-methylethyl)N-phe
nylacetamide; trifluralin, alpha,alpha,alpha-trifluoro-2, 6-dinitro-N,
N-dipropyl-p-toluidine; simazine, 2-chloro-4,6-bis(ethylamino)-s-tria
zine; propazine, 2-chloro-4,6-bis(isopropylamino)-s-triazine; fonofos,
O-ethyl S-phenyl ethylpbosphonodithioate; metribuzin, 4-amino-6-(1,1-
dimethylethyl) -3-(methylthio)-1,2,4-triazin-5(4H-one] and two atrazin
e metabolites, deethylatrazine, 2-amino-4-chloro-6-isopropylamino-s-tr
iazine (DEA) and deisopropylatrazine, 2-amino-4-chloro-6-ethylaminostr
iazine (DIA) were detected. Atrazine, cyanazine, DEA and DIA levels we
re greater than 1 mug/L. Atrazine remained above the maximum contamina
nt level for potable water of 3 mug/L throughout the period of investi
gation. The pesticide response to spring and summer runoff events was
much less pronounced at Willow Lake, a 284 ha impoundment. Ten of 12 p
esticides and two atrazine metabolites in Maskenthine Lake were also d
etected in Willow Lake; however, concentrations did not exceed 1 mug/L
. After the spring flush of pesticides in May and June, concentrations
decreased until the following spring. Ratios of DEA to atrazine and D
IA to atrazine remained relatively constant suggesting that appreciabl
e amounts of biodegradates were not produced. Apparent half-lives were
calculated from observed concentration decreases that appeared to fol
low first-order kinetics. Atrazine was the most persistent agrichemica
l (t1/2 = 193, t1/2 = 124) introduced in the spring runoff events. Ext
racted pesticide levels were higher in bottom cores from Maskenthine L
ake than from Willow Lake. Differences in pesticide levels in the two
lakes were related to watershed slope, soil drainage capacity, landuse
, and rainfall.