13C-NMR spectroscopy was applied to the evaluation
of soil-bound residues of the fungicide cyprodinil (4-cyclopropyl-
6-methyl-2-phenylaminopyrimidine). A mixture of the
13C-
and 14C-labeled fungicide was used to obtain
structural
information as well as information on the quantitative
distribution in the various fractions. Bound residues
were
accumulated by a 6-month incubation of the labeled
compound with a clay loamy soil. Depending on the
concentration of [13C]cyprodinil (500, 250, 80, and
3 mg/kg),
binding ranged from 18% to 54% of the initial
radioactivity.
After methanol extraction of soil (10 g dry weight) treated
with
500 mg/kg (5.0 mg) of the fungicide, the amount of unextracted bound material was equivalent to 0.9 mg of
13C-labeled cyprodinil. Upon fractionation, 0.21 mg of
the
bound fungicide was found in the dialyzed humic acid,
0.13 mg in fulvic acid (after extraction with
CH2Cl2), and 0.24
mg in humin. The methylene chloride extract from
fulvic
acid mainly contained unchanged cyprodinil (0.21 mg) that
was apparently sequestered in soil by physical forces.
The humic acid fraction was dissolved in a 1% solution
of
NaOD and examined by 13C-NMR. The NMR
spectrum
of the material from the control sample exhibited all the
characteristic features of a typical humic acid. When
the
control humic acid was spiked with cyprodinil labeled
uniformly with 13C at the phenyl ring, four additional
signals
at 121.9, 124.4, 131.8, and 143.4 ppm could be
distinguished
in the NMR spectrum. However, when humic acid
originated from the soil that was incubated with the
phenyl-labeled fungicide, only two strong NMR signals, at 122.5
and 131.8 ppm, and two less significant signals around 142
and 162 ppm were observed. The difference in the
signal
pattern indicated cleavage of the cyprodinil molecule
between
the aromatic rings and independent binding of the phenyl
and pyrimidyl moieties to humic acid.
The fungicide cyprodinil [4-cyclopropyl-6-methyl-2-(phenylamino)pyrimidine] labeled with 14 C in either the phenyl or the pyrimidyl ring was incubated with four different soils under various conditions to evaluate the formation of bound residues and their subsequent plant uptake. About 60% of the initially applied radioactivity was bound to nonsterile soils within 90-180 days, whereas negligible binding was observed under sterile and anaerobic conditions. More binding was observed at higher soil pH, cation exchange capacity, and organic carbon and nitrogen contents. When spring barley was grown in the methanol-extracted soil, the plant uptake of bound residues amounted to about 0.2% for the phenyl label and 1.2% for the pyrimidyl label. The difference indicated that the pyrimidyl moiety was detached from the cyprodinil molecule and taken up more readily.
The effect of selected pesticides, monocrotophos, chlorpyrifos alone and in combination with mancozeb and carbendazim, respectively, was tested on nitrification and phosphatase activity in two groundnut (Arachis hypogeae L.) soils. The oxidation of ammonical nitrogen was significantly enhanced under the impact of selected pesticides alone and in combinations at 2.5 kg ha(-1) in black soil, and furthermore, increase in concentration of pesticides decreased the rate of nitrification, whereas in the case of red soil, the nitrification was increased up to 5.0 kg ha(-1) after 4 weeks, and then decline phase was started gradually from 6 to 8 weeks of incubation. The activity of phosphatase was increased in soils, which received the monocrotophos alone and in combination with mancozeb up to 2.5 and 5.0 kg ha(-1), whereas the application of chlorpyrifos singly and in combination with carbendazim at 2.5 kg ha(-1) profoundly increased the phosphatase activity after 20 days of incubation, in both soils. But higher concentrations of pesticides were either innocuous or inhibitory to the phosphatase activity.
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