Degradation products of chlorsulfuron, chlortoluron, diuron, fluometuron, i
soproturon, linuron, metabenzthiazuron, metobromuron, and monuron formed in
the gas chromatographic injector have been used for identification of the
respective herbicides. Mass spectra of the derived compounds were obtained
with a quadrupole mass spectrometric detector working in scan mode (20-450
amu). The compounds generated often depended on the solvent used for phenyl
urea herbicide injection (ethanol, methanol, dichloromethane, and acetonitr
ile). When methanol and ethanol were used as solvents the major products fo
rmed from phenylureas were carbamic acid esters. When acetonitrile or dichl
oromethane were used the main derivatives were phenylisocyanates. Chlorsulf
uron and metabenzthiazuron, however, generated a triazine plus a phenylsulf
onamide and a benzothiazolamine, respectively, irrespective of the solvent
used. Linuron and diuron behaved similarly and gave degradation products wi
th the same mass spectra. The thermal reactions occurred instantaneously in
the injector block and were promoted by the high temperature selected (300
degreesC).
Determination of the compounds derived from urea herbicides, by use of a 30
m BP10 column and a selected ion registering (SIR) program based on two or
three ions, can be used for sensitive detection of the presence of urea he
rbicides in environmental extracts. With standards in methanol instrument d
etection limits ranged from 0.1 pg for chlorsulfuron (detected as 2-chlorob
enzensulfonamide) to 1 pg for monuron and metobromuron (both detected as th
eir carbamic acid methyl esters). RSD were below 9% at the 5 ng L-1 level.
The response was linearly dependent on quantity (r > 0.9986) in the 5 ng L-
1 to 25 mug L-1 range. Unequivocal identification of some phenylurea herbic
ides was not always possible because some herbicides with similar structure
s, for example diuron and linuron, gave the same derivative.