Dr. Ishii, Director of Chemical Analysis Research Center, won the Award of
Pesticide Science Society of Japan in 2003. With the increase in the kinds
of pesticides being used in agricultural production, however, it has become
impossible to monitor pesticide residue levels in food effectively and meaningfully
by means of the methods used for individual pesticides. The only reasonable
approach to monitoring the pesticide residues is to simplify the analyses by
developing methods that measure more than one pesticide at a time. For such
a purpose, Dr. Ishii has improved and developed the existing pesticide residue
analysis methods as follows:
(1) Application of high-performance liquid chromatography (HPLC) to pesticide
residue analysis.
HPLC was used for the improvement in sensitivity and accuracy of the residue
analyses of strong polar pesticides and ionic pesticides. The method for measuring
the amount of the combination of methyl benzimidazol-2-ylcarbamate (MBC) that
thiophanate methyl (TM) in crops are chemically converted and MBC in crops
is adopted as an official method of TM. He found MBC and two oxygen analogues
of TM in the photo-degradation products of TM. He developed analysis method
that was able to measure TM and the main degradation products simultaneously.
Average recoveries for TM and its degradation products from fortified samples
were 70~104% at 0.5 ppm levels. The minimum detectable amount was ca 5 ng for
TM and its degradation products.
He also tried to develop an analysis method for ionic herbicides such as
paraquat and diquat that used HPLC equipped with an ultraviolet detector. The
minimum detectable amount of paraquat was 0.1 ng at 254 nm. Diquat was also
detected in subnanogram quantities. The detection limit of paraquat was 0.0005
ppm in 100-g crop samples and 0.002 ppm in 25-g soil samples. Recoveries were
80% to 104% from crop samples fortified at 0.1 to 0.5 ppm and 70% to 100% from
soil samples fortified at 0.4 to 2 ppm. The sensitivity of the new analysis
method is at least ten times higher than that of the classical colorimetric
method.
(2) Rapid cleanup procedure with a charcoal-Florisil minicolumn for multiresidue
analysis.
A simple and efficient cleanup procedure for gas chromatographic determination
of pesticide residues was developed by using a charcoal-Florisil minicolumn.
The pesticide residues were extracted with methanol, partitioned into toluene,
cleaned up with the minicolumn, and determined by gas chromatography. Recovery
data were obtained from 15 crops fortified with 25 pesticides at their tolerance
levels. Recoveries of 23 pesticides were higher than 90%. The detection limits
were 0.01 to 0.02 ppm for organophosphates, 0.05 ppm for carbamates and synthetic
pyrethroids, and 0.005 ppm for organochlorines.
(3) Application of preparative liquid chromatography to a residue analysis
cleanup procedure.
Preparative chromatography, especially gel permeation chromatography (GPC),
was evaluated as a possible cleanup technique for determining pesticide residues.
The residues were cleaned up with a GPC system in which Bio-Beads SX-3 was
used as the gel. Pesticides were determined by GC-flame photometric detector,
GC-thermionic alkali flame ionization detector, and Hall electrocoductivity
detector. Recovery data are presented for more than 60 pesticides (organophosphates,
carbamates, synthetic pyrethroids, organochlorines) in 19 crops. Average recoveries
ranged from 70% to 120% at 0.1- to 10 ppm fortification levels. The detection
limits ranged from 0.005 to 0.05 ppm.
(4) Immunochemical assay of pesticide residue
Highly reactive monoclonal antibodies for bensulfuron-methyl, pyrazosulfuron-ethyl,
thiobencarb, and mefenacet were prepared. With the antibodies, a simultaneous
competitive enzyme-linked immunosorbent assay (ELISA) was carried out. The
assay provided the tool for the determination of residues of the four herbicides
in water without any pre-treatment of the water sample. Determination concentrations
ranged from 0.2 to 1.5 ng/ml for bensulfuron-methyl, 0.2 to 4.5 ng/ml for pyrazosulfuron-ethyl,
0.2 to 3.4 ng/ml for thiobencarb, and 0.2 to 4 ng/ml for mefenacet.