1
214
T. Ohshiro et al. / Phytochemistry 52 (1999) 1211±1215
3. Experimental
The enzymatic reaction to release the volatile halo-
genated compounds was carried out according to the
procedure described previously (Itoh & Shinya, 1994).
The reaction mixture contained 0.1 M potassium phos-
phate buer (pH 6.8), 10 mM KBr, 1 mM oxaloacetic
acid, 1 mM H O and 0.0023 units/ml BPO from U.
lens in a total volume of 30 ml. A vial (30 ml head-
space) containing the reaction mixture was allowed to
stand for 2 h at 208C. A control was performed with-
out BPO. The gas phase was analyzed by the head-
space method using a GC-MS instrument. Analysis of
the products was performed with a Hewlett Packard
gas chromatograph (HP5890-II) ®tted with a capillary
column (Rtx-volatiles, 60 m: 0.25 mm id: 1 mm) and a
Hewlett Packard mass spectrometer (HP-5971A).
Ulvella lens was grown on transparent, colorless
acrylic resin plates (580 Â 300 Â 0.5 mm) for approxi-
mately two months at the Hokkaido Aquaculture
Development Authority, Kayabe-gun, Hokkaido, in
early spring, then scraped by spatulas and stored at
208C until use. Enzyme puri®cation was performed
below 158C. Algal cells (500 g, wet weight) were sus-
2
2
�
pended in 500 ml of 50 mM Tris-SO buer (pH 7.4)
4
and disrupted by f 0.5 mm glass beads through a
Dyno-mill homogenizer (Willy A. Bachofen, Basel,
Switzerland) ®ve times. The cell-free extract was
obtained by centrifugation at 12,000 Â g for 30 min,
and dialyzed against 50 mM Tris-SO buer (pH 7.4).
4
The dialyzed enzyme solution was applied onto a
DEAE-Sepharose Fast Flow column ꢀf 3.6 Â 30 cm)
equilibrated with 50 mM Tris-SO buer (pH 7.4). The
4
Acknowledgements
column was washed with the same buer, and the
enzyme was eluted with the same buer containing 0.8
M NaCl at a ¯ow rate of 60 ml/h. The active fractions
We thank the Hokkaido Aquaculture Development
Authority for cultivation and supply of U. lens cells,
and Dr. R. Wever, University of Amsterdam, for
instruction in the phenol red assay method of BPO ac-
tivity. We are also grateful to Dr. Hideharu Kondoh,
Hokkaido Institute of Environmental Science, for use
of the GC-MS instrument. Part of this work was ®nan-
cially supported by a Grant-in Aid for Scienti®c
Research from the Ministry of Education, Science,
Sports and Culture of Japan.
were combined, dialyzed against 50 mM Tris-SO buf-
4
fer (pH 7.4) containing 0.8 M (NH ) SO , and applied
4
2
4
onto a Phenyl Toyopearl column ꢀf 1.8 Â 19 cm) equi-
librated with the dialysis buer. The column was
washed with the same buer and eluted with a linear
(
SO buer (pH 7.4), using a ¯ow rate of 10 ml/h. The
NH ) SO gradient (from 0.8 to 0 M) in 50 mM Tris-
4 2 4
4
active fractions were combined and concentrated by
ultra®ltration. The concentrated enzyme was applied
to a Toyopearl HW-55 gel ®ltration column ꢀf
3
.6 Â 30 cm) equilibrated with 50 mM Tris-SO buer
4
(
pH 7.4) containing 0.1 M KCl at a ¯ow rate of 3 ml/
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