7598
J . Org. Chem. 1998, 63, 7598-7599
been developed. Since approximately 108-109 bacteria are
present in 1 g of soil,11 this covers a wide genetic diversity
suitable for initial screening. Hydrogen peroxide was chosen
as selecting agent, because it is a potent inductor of
peroxidase transcription; however, it may also select some
strains with catalase activity. In contrast to current screen-
ing procedures, in which the substrate is administered as
the only carbon, sulfur, or nitrogen source at an early stage
of the growth cycle, in our protocol, the substrate is added
as a selecting agent in addition to all the other nutrients
necessary for the normal growth of the bacteria.
Our growth medium was either a full (Plate Count Agar,
Difco Laboratories) or a minimal (Dworkin et al.12) medium,
which was supplemented with the necessary trace elements.
The rationale behind this strategy was that most of the
substrates will not be accepted as a sole nutrient source by
bacteria, but such substances are still toxic enough to induce
the detoxification in sufficient bacteria, which have the
necessary genes to express the required peroxidase. More-
over, the material may be added at any stage of the bacterial
growth cycle to allow for more diversity in the control of the
biotransformation under examination.
The present screening procedure with H2O2 resulted in
four distinct species, which have been subjected to charac-
terization by the sequencing of the first 300 base pairs of
their small subunit ribosomal RNA gene (16s/18s) with the
Taq-cycle-DyeDeoxy-terminator technique13 (ABI division of
Perkin-Elmer, Weiterstadt). The results show that three
Bacillus spp. have been isolated that were not identical.
Morphological and 18s-rRNA sequence data show that the
fourth strain isolated is most probably a Paecilomyces sp.
The Bacillus strain, which gave the best results in regard
to the kinetic resolution of the organic hydroperoxides, was
more rigorously characterized and determined to be a
Bacillus subtilis strain.
Kin etic Resolu tion of Ch ir a l Hyd r op er oxid es:
Hyd r ogen -P er oxid e-Med ia ted Scr een in g of
P er oxid a se-Active Soil Ba cter ia
Waldemar Adam,† Barbara Boss,‡ Dag Harmsen,§
Zoltan Lukacs,*,†,‡ Chantu R. Saha-Mo¨ller,† and
Peter Schreier‡
Institutes of Organic Chemistry and of Pharmacy and
Food Chemistry, University of Wu¨rzburg, Am Hubland,
D-97074 Wu¨rzburg, and Institute of Hygiene and
Microbiology, University of Wu¨rzburg, J osef-Schneider-Str. 2,
D-97080 Wu¨rzburg, Germany
Received September 9, 1998
Hydroperoxides have been used frequently in asymmetric
oxidation;1,2 in fact, recently, enantiomerically pure hydro-
peroxides have become important as oxidants in the syn-
thesis of optically active compounds.3a,b Since by conven-
tional chemical means it has been difficult to obtain
enantiomerically pure products, nowadays the popularly
used enzymes in preparative organic chemistry have been
successfully employed in view of their high degree of
enantioselectivity and catalytic activity.4 By this means,
optically active hydroperoxides were obtained with lipases,5
lipoxygenase,6 and horseradish peroxidase.7 Most recently,
a chemically modified subtilisin enzyme, namely selenosub-
tilisin, was successfully applied to the kinetic resolution of
racemic hydroperoxides.8 Nevertheless, large quantities of
pure enzyme, which are necessary for preparative applica-
tions, are difficult to come by and expensive.
These disadvantages are to be contrasted with whole cell
systems (bacteria, fungi, and plant/animal cells), which
circumvent such problems since they are potentially avail-
able in large quantities through self-replication. No work
along these interdisciplinary lines is currently available on
peroxidase systems in bacteria and fungi, certainly not for
the kinetic resolution of racemic hydroperoxides.
All of the bacterial species mentioned above were incuba-
ted with 0.07 mmol of the particular racemic hydroperoxide
for the kinetic resolution of the hydroperoxides (Scheme 1):
Sch em e 1. Kin etic Resolu tion of Hyd r op er oxid es 1
by Soil Ba cter ia or F u n gi
As a matter of fact, most of the focus in recent years has
been set on the elucidation of the genetic expression of
peroxidases during the response to stress factors.9,10 Here,
we communicate our results of the first kinetic resolution
of organic hydroperoxides by soil bacteria and fungi.
First, an adequate screening procedure to select suitable
soil bacteria for the biotransformation of hydroperoxides had
* To whom correspondence should be addressed. Fax: +49-931-8885484.
E-mail: zoltan@pzlc.uni-wuerzburg.de.
For these experiments, the (1-phenyl)ethyl (1a ) and 1-(1-
phenyl)propyl (1b) hydroperoxides were used as model
substrates. The results are summarized in Table 1.
† Institute of Organic Chemistry.
‡ Institute of Food Chemistry.
§ Institute of Hygiene and Microbiology.
(1) J ohnson, R. A., Sharpless, B., Ojima, I., Ed. Catalytic Asymmetric
Synthesis; VCH: Weinheim, 1993; pp 103-158.
(2) Adam, W.; Richter, M. J . Acc. Chem. Res. 1994, 27, 57-62.
(3) (a) Shum, W. P. S.; Saxton, R. J .; Zajacek, J . G. US Patent 5663384,
1997. (b) Adam, W.; Korb, M. N.; Roschmann, K. J .; Saha-Mo¨ller, C. R. J .
Org. Chem. 1998, 63, 3423-3428.
(4) Adam, W.; Lazarus, M.; Saha-Mo¨ller, C. R.; Weichold, O.; Hoch, U.;
Ha¨ring, D.; Schreier, P. Biotransformations with Peroxidases. In Advances
in Biochemical Engineering/ Bio-technology/ Biotransformations; Faber, K.,
Ed.; Springer-Verlag: Heidelberg, in press.
Two of the isolated bacterial species showed slow conver-
sion of the hydroperoxides and poor enantiomeric excess for
both the alcohol and the hydroperoxide (see entry 6 for an
example). Thus, these two strains were not considered for
further experimentation. The Paecilomyces sp. (entry 4)
showed much faster conversions, so that after only 80 min
as much as 92% of the hydroperoxide 1a was converted and
an enantiomeric excess (ee) of 79% of the (R)-hydroperoxide
1a was achieved (entry 4). The best results were obtained
with B. subtilis (entry 1), which converted 64% of hydro-
(5) Baba, N.; Mimura, M.; Hiratake, J .; Uchida, K.; Oda, J . Agric. Biol.
Chem. 1988, 52, 2658-2687.
(6) Datechva, V. K.; Kiss, K.; Solomon, L.; Kyler, K. S. J . Am. Chem.
Soc. 1991, 113, 270-274.
(7) Adam, W.; Hoch, U.; Lazarus, M.; Saha-Mo¨ller, C. R.; Schreier, P. J .
Am. Chem. Soc. 1995, 117, 11898-11901.
(11) Blaine Metting, F., J r. Soil Microbiological Ecology; Marcel Dekker
Inc.: New York, 1993.
(12) Dworkin, M.; Foster, J . W. J . Bacteriol. 1958, 75, 592-603.
(13) Harmsen, D.; Heesemann, J .; Brabletz, T.; Kirchner, T.; Mu¨ller-
Hermelink, H. K. Lancet 1994, 343, 1288.
(8) Ha¨ring, D.; Herderich, M.; Schu¨ler, E.; Withopf, B.; Schreier, P.
Tetrahedron: Asymmetry 1997, 8, 853-856.
(9) Storz, G.; Tartaglia, L. A.; Ames, B. N. Science 1990, 248, 189-194.
(10) Demple, B. Annu. Rev. Genet. 1991, 25, 315-337.
10.1021/jo9818327 CCC: $15.00 © 1998 American Chemical Society
Published on Web 10/16/1998