Vol. 163, No. 1, 1989
BIOCHEMICAL AND BIOPHYSICAL RESEARCH COMMUNICATIONS Pages 476-480
August 30, 1989
Determination of Multiple Forms of Cytochrome P-450 in Microsomes From the Digestive Gland of Crvptochiton stelleri Daniel
Schlenk
and Donald
R. Buhler
Toxicology Program Oregon State University Corvallis, Ore 97331 Received
July
17,
1989
Polyclonal antibodies raised against purified trout cytochromes P-450 (P-450) IM2 (anti-IM2) and h!+i4b (anti-bM4b) were used in Western blot analyseswith digestive gland microsomes from control and /.3- naphthoflavone (BNF)-treated gumboot chitons Crvntochiton stelleri. An increase and decrease in staining intensity subsequent to treatment with anti-LM4b and anti-W2, respectively, was observed in digestive gland microsomes from BNF-treated chiton. Thus, there appears to be at least two forms of P-450 in microsomes from the digestive gland of Crvntochiton; one of which is induced by BNF and perhaps is involved in benzo(a)pyrene (BP) biotransformation, and another form which is inhibited by BNF. 0 1989 Academic Press,
Inc.
Phase well
I biotransformation
as
detoxify
bioactivation
to
xenobiotics
which
to lead
animal
same
either
essential the
of the
daes not
possess to more
with
detoxication
enzymatic
pathways
dynamic
number
of
unpublished
has
relatively
toxic In
data).
an attempt
copes with the toxic chemicals several xenobiotic biotransformation Cytochrome
(2). of
Crwtochiton
greater OOW291x/89 Copyright All rights
in
P-450 and
animals
to that
was observed pretreated
better
with
476
the
enzymes over
animals to
which
survive
contain
bromophenols how
a
(Yates, this
animal
the contribution of species was examined
from (BPH)
cytochrome
the
ecosystem.
on algae as
are
or has enzymes
understand
hydroxylase
toxicity
with
equipped
it encounters, systems in this
$1.50
0 1989 by Academic Press, Inc. of reproduction in any form reserved.
such
of
habitat
Consequently,
marine
feed
in microsomes
benzo(a)pyrene
the
an advantage
be better
as
ratio
a given
of detoxication
to
chemicals
the
equipped
species.
would
shown
in is
such as the
been
of
may have
toxic
environment
stelleri
to bioactivate
understanding
that
enzymes
chemicals
Crvntochiton
in
chemical
bioactivate
potential
two animals
animal
which
in a chemically
the
Determination
assuming
toxicant,
to detoxication
that
is
Therefore,
the
have
(1).
detoxication
of any xenobiotic. exposed
pathways
the
digestive
was
significantly
P-450
inducer,
gland j3-
BIOCHEMICAL
Vol. 163, No. 1, 1989
naphthoflavone
(BNF)
noncarcinogenic Since
the
multiple gland
of ,these
raised
against
two
trout
were
in
trout,
P-450
catalytic shown
forms
to
reactive
be
used
trout
liver
(8)
gene
family
(9).
MATERIALS
and
for
IM4b
for
the
are there
BNF.
oxidation
LM4b has been
possibly
representing
in most research
is
from
shown
the
possess
Isoform of
aflatoxin
livers two
LM2 has Bl
expressed
from
of forms
different to
the
to be the BNF-inducible
a protein
to
antibodies
These to
was
in microsomes
Polyclonal
shown
animal
any quantitative
immunoquantitation. been
a
hydrocarbon
present
isolated
specificities.
while
this
and if P-450
have
substrate
of
as
and BP.
enzyme with
of
used
to be inducible
of this
forms and
is
polyaromatic
purpose
treatment
as probes
IM2
responsible
epoxide
appears the
forms
purified
activities
inducing
of Crvntochiton after
chemical
as 3-methylcholanthrene
chiton,
whether
latter
P-450
activity
the
digestive
change rainbow
such
P-450
including
determine
of
for
contaminants cytochrome
species, from
This
(2).
substitute
environmental
AND BIOPHYSICAL RESEARCH COMMUNKATIONS
been more
form the
in
P450IB
AND METHODS
Chemicals fi-Naphthoflavone (BNF) was purchased from Aldrich Chemical and [G-3H]-Benzo(a)pyrene Company (Milwaukee, from ICN WI) (BP) Radiochemicals (Irvine, CA). [14C-7,10]-BP was obtained from Amersham (Arlington Heights, IL). All other biochemicals were purchased from Sigma Chemical Company (St. Louis, MO). For induction studies, 10 Animal treatment and microsome nrenaration animals (5 treated and 5 control), obtained by using SCUBA from subtidal rock jetties in Newport OR, were not fed for 2 weeks prior to treatment. Treated animals were dosed orally at 10 mg/kg with /3-naphthoflavone (BNF) in corn oil three times a week for three weeks. Control animals received oil. only corn Animals were sacrificed by freezing at -2OOC for approximately 20 min and dissected. Microsomes were prepared at 4OC by a modified procedure as described in Livingstone and Farrar (3). Tissues were placed in a 1:4 w/v ratio of 20 mM Tris-HCl buffer, pH 7.6, containing 0.5 M sucrose, 0.15 M KGl, 1 mM ethylenediaminetetraacetic acid (EDTA), 1 mM dithiothreitol and 0.1 mM CD=) were carried out phenylmethylsulfonylfluoride (PMSF). Homogenizations using a teflon Potter-Elvehjem homogenizer. The homogenate was centrifuged at 12,000 x g for 20 min in a Sorvall RC-PB refrigerated centrifuge. Following a second 12,000 x g spin of the supernatant, a final centrifugation at 100,000 x g for 90 min was performed. The microsomal pellet was resuspended in a storage buffer which contained 20 mM Tris-HCl pH 7.6, 20% w/v glycerol, 1 mM EDTA, 1 mM DTT, and 0.1 mM were stored at -8OOC until needed. PMSF. Unused microsomes Electrouhoresis and immunoblotting Electrophoresis of microsomal proteins was performed using 8.0 % separating and 3.0 % stacking polyacrylamide gels in the presence of sodium dodecyl sulfate (SDS) (4). Following electrophoresis, the separated proteins were transferred via electroblot to nitrocellulose sheets following a modification of the method of Towbin et al. (5) and stained by a modification of the method of Burnette (6) using polyclonal antibodies raised against purified trout cytochrome P-450s IM2 and I&b (7). The nitrocellulose was exposed to Kodak XAR-5 X-ray film for 7 days at - 80°C. Relative quantitation of autoradiograms was performed utilizing laser densitometry (Zeineh). 411
BIOCHEMICAL
Vol. 163, No. 1, 1989
AND BIOPHYSICAL RESEARCH COMMUNICATIONS
RESULTS AND DISCUSSION Microsomes
from
purified
trout
observed
to
react
BNF-treated control
antibodies to
those
chitons
to
observed
possessed
antibodies chiton
greater
relative microsomes
with
trout
data
suggests
protein
m4b, at
observed shown
is,
be present
within
A similar
activity pretreatment
was
observed caused
in
in
and
gland
BNF-treated
in
from the
of for
the
I ,
Figure
1.
2.
this
from
P-450
the
chiton. content
content
and
(8).
BNF
livers form
23456 , ,,I
Western blot analysis of microsomes from the digestive glands of control and BNF treated chiton stained with anti-trout LM 4b' Lane l-3, control, 100 yg protein; Lane 4-6, BNF, 100 1J.g protein; Lane 7-10, purified trout LM4b, 2.0, 1.0, 0.5, 0.2 pm01 protein.
were
P-450
p-450
trout
the
BPH
activities
Western blot analysis of microsomes from the digestive glands of control and BNF-treated chiton stained with anti-trout LM2. Lane 1-3, control microsomes, 100 ng protein; Lane 4-6, BNF microsomes, 100 ng protein; Lane 7, control cytosol, 100 1.18 protein; Lane BNF cytosol, 100 ng protein; Lane 9-11, purified 0.5, 1.0 pm01 protein. trout LM2, 0.2,
478
then
augmented
LM2 and a
I
-54K Figure
from
and
while
between
IM4b
function
BP,
Crvntochiton
microsomes
rainbow
in
in
chitons,
constitutive
with protein
equivalent
associated
relationship
microsomes
a decrease
the
biotransformation
digestive
was
stained
P-450
bands darker
BNF-treated
when
responsible
anti-LM2
these
Assuming
exist
from
consistently
3).
is
in
a much
with
reaction
P-450
be
chitons. greater
(2).
in
with
Although is
and
microsomes
Conversely,
anti-IM4b
of
may
BPH was significantly unchanged
with
forms
daltons
BNF-treated
of (Figure
involved
multiple
60,000
in to
that
that
3). band
was
observed
along
staining
band control
was
of
samples.
reacted
also
(Figure
levels
both
gland
BNF-treated
which
60,000 anti-m2
each
controls
in
intensities
against
A single
Digestive
intensities,
to
antibodies
daltons
with 1).
BNF treated
from
at
stained
with
1 and 2).
60,000
(Figure greater
variable
reacted
A band
samples
possessed
have
at
2).
daltons
relative
appeared
gland (Figures
anti-IM4b
(Figure
at 54,000
chitons
than
with
BNF-treated
band
control
digestive
LM2 and w4b
samples and
darker
chiton
P-450s
8,
78 I
I
9 10 II
BIOCHEMICAL
Vol. 163, No. 1, 1989
AND BIOPHYSICAL RESEARCH COMMUNICATIONS
: Errol P < 0.01 t
LM-2
LY-4b Enzyme
Figure
3.
Relative staining intensities of microsomes from the digestive glands of control and BNF-treated chitons stained with anti-trout LM2 and LM4b. Each value represents the mean of three sample replications from the same preparation +- S.D.
significant
increase
in
differences
in
content,
BNF-treated
and control
The
is
suggest
biosynthesis
when
antibodies
to
be structurally I&b
only
indiscriminate than against with probes
in
anti-l.M4b. a specific other
P45Os
as a more
In
accurate
studies,
P-450 measure
role
isozyme
to
the of
led
in
to
no
BPH between
and
primitive
Gonzalez in
to include
xenobiotic
steroid
metabolites.
Since
crossreacted that
the
from
invertebrates two bands, that
thus
(9)
a function
with
the
enzyme
must
to fish.
more
antibodies shown
P450 isozymes
anti-
may be more
recognizing
been
with
whereas
anti-I&i2
polyclonal have
a
to
sites raised
crossreact
use of mRNA quantitation
individual 479
P-450
appears
identification
led
Nebert
implication
It
mammalian has
which
chiton
plant
reacted
protein.
purified which
its
evolution
anti-m2
epitope
of
of
a strong
in
serving
encounter
forms
through
one its
already
to
is
that
nmol/mg)
hypothesis
trout
conserved
LH4b
differences
broadened
began there
recognized
the P-450,
purified
interesting
(0.11
evolution,
protein,
is
P-450
animals
form
significant
(8).
with
in
the
BP metabolizing but
cytochrome
early
metabolism
It
of
consistent that
invertebrate
the fish
content
large
herbivore, who
P-450
with (9).
cDNA At any
Vol. 163, No. 1, 1969
rate, with
the
two proteins
anti-LM2 The
must to
environments whether
induction
data
should
organic of
P-450
a better
in
some structural P-450
More
natural allow
chiton
as
(10).
of
observed of
serve
effect
AND BIOPHYSICAL RESEARCH COMMUNKATIONS
share
measurement
suggested
BIOCHEMICAL
a
digestive
research
in
marine
indicator
of
needs
chemicals can
occur
understanding
samples
stained
similarities.
induction
possible
gland
marine
has
pollution
to be performed on
in
organisms focusing
molluscs
nonpolluted of how marine
in to
environments. organisms
been marine on the
determine These cope with
xenobiotics. ACKNOWLEDGMENTS We would like to thank Dr. Lavern J. Weber of the OSU Hatfield Marine Science Center for the use of the facilities and Kenneth Yates for his collection and maintenance of the chitons. This research was supported by grants from the National Institutes of Environmental Health Sciences No. ES00210, ES03850 and ES07060. This paper was issued as Technical Paper No. 8935 from Oregon Agricultural Experiment Station. REFERENCES (1) Buhler, D.R. and Williams, D.E. (1988) Aquat. Toxicol. 11, 19-28. (2) Schlenk, D. and Buhler, D. R. (1988) Aquat. Toxicol. 13, 167-182. (3) Livingstone, D. R. and Farrar, S. V. (1984) Sci. Total Environ. 39, 209-235. (4) Laemmli, U. K. (1970) Nature 227, 680-685. (5) Towbin, H., Staehelin, T., and Gordon, J. (1979) Proc. Natl. Acad. Sci. USA, 76, 4350-4354. (6) Burnette, W. N. (1981) Anal. Biochem. 112, 195-203. (7) Miranda, C. L., Wang, J. L., Henderson, M. C., and Buhler, D. R. (1989) Arch. Biochem. Biophys. 268, 227-238. (8) Williams, D. E., and Buhler, D. R. (1984) Biochem. Pharm. 33, 37433753. (9) Nebert, D.W., and Gonzalez, F.J. (1987) Ann. Rev. Biochem. 56, 945-93. (10) Payne, J. F., Fancey, L. L., Rahimtula, A. D., and Porter, E. L. (1987) Comp. Biochem. Physiol. 86C, 233-245.
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