Vol. 120, No. 1, 1984
BIOCHEMICAL
AND BIOPHYSICAL RESEARCH COMMUNICATIONS
April 16, 1984
Pages
286-290
FLUORESCENCE CHARACTERIZATION OF THE LOW pH-INDUCED CHANGE IN DIPHTHERIA TOXIN CONFORMATION: EFFECT OF SALT Michael
G. Blewitt, Raghupathy
Department Received
March
7,
Jian-Min Zhao, Brian McKeever, Sarma and Erwin London*
of Biochemistry, Stony Brook,
S.U.N.Y. at Stony N.Y. 11794
Brook,
1984
We have examined the effect of pH on diphtheria toxin conformation using intrinsic protein fluorescence and a new fluorescence quenching method. In aqueous solutions, fluorescence indicates toxin conformation undergoes a drastic change at low pH. This conformational change is closely associated with a switch from a hydrophilic conformation to a hydrophobic one, as judged by quenching-detected detergent binding. In the absence of NaCl these changes occur around pH 4-4.5. However, in 150 mM NaCl the conformational change occurs in the pH 5-5.5 range, close to the pH the toxin is expected to encounter in endosomes and lysosomes. Therefore, the conformational change observed at low pH is likely to be physiologically signficant.
It
is
now clear
virus
and protein
virus
and influenza
endocytosis, endosomes low
and
(4)
virus then
switch study
binding
into
enter
cells.
cells
penetrating
that
similarities toxin,
to
membrane
latter
of
step
is
Semliki
vesicles,
to
significant
Forest
undergoing
accomplished
hydrophobicity,
becomes
between
receptors,
acidic
conformation
toxin
toxin,
strong
attaching
a hydrophilic
indicated
by normal
by
This
are
Diphtheria
the
(l-4). from
there
either
partly
by a
a hydrophobic
inferred
from
the
pH 4-4.5
below
one. Triton range
*
Our secondary
recent and
concentration
preliminary tertiary
previous
is results
hydrophobic
Copyright All rights
structure
around
the
noted
pH of only
above.
pH 5, close
should
have In
(5).
significant
whom correspondence
0006-291X/84
studies
influences
hydrophobicity
*To
entry
or lysosomes
A previous
in some cases
toxin
pH-induced
X-100
that
the
below
to physiological
be addressed.
$1.50 286
that
this
report,
low
pH 4-4.5, in
150 values.
pH alters we find
conformational
However,
0 1984 by Academic Press. Inc. of reproduction in any form reserved.
shown
switch. in
that Without
agreement
mM NaCl
toxin
toxin
salt NaCl
with
the
becomes
Vol.
120,
No.
1,
BIOCHEMICAL AND BIOPHYSICAL RESEARCH COMMUNICATIONS
1984
MATERIALS AND METHODS Crude diphtheria toxin was purchased from Connaught Laboratories (Ontario, Canada). Trypsin, N-e -p-tosyl-L-lysine-chloromethylkentone, and Brij 96 (an oleyl polyoxyethylene ether detergent) were purchased from Sigma Chemical. All other chemicals were reagent grade. Purified toxin was isolated as described previously (6). The dimer toxin fraction with bound ApUp (a natural dinucleotide ligand (7)) was used for further experiments. Only a few percent of nicked toxin was present as judged by SDS gel electrophoresis:l -fP otein concentration was calculated using a value of E 28C = 55,300 cm M for ApUp-bound toxin derived from published values for aromatic amino acids and ApU (8). (Lowry assay gave roughly 20% higher values). Toxin nicked between the A and B subunits was prepared by incubation of 10.8 mg intact toxin in 0.75 ml of 1.3 ug/ml trypsin /50 mM Tris-Cl pH 7.2/2mM CaCl . After lh 5 ul of 1 mg/ml N-a-p-tosyl-L-lysinechloromethyl i?etone was added. Then toxin was reisolated by chromatography on a 2.5 cm x 95 cm column of Sephacryl S-200 using a buffer of 50 mM Tris-Cl pH 7.2/l mM EDTA 0.02% (w/v) NaN3. SDS gel electrophoresis showed that nicking was complete. Dibrominated Brij 96 was synthesized by titration of an aqueous solution of Brij 96 with concentrated bromine water. The reaction was over in 5 seconds as monitored by loss of bromine color. Following excess bromine by we found a sharp endpoint to the titration indicating that 70% of Brij kg3 molecules contained double bonds in their hydrocarbon chains (the site of bromination). The Brij 96 used for further experiments was brominated to 80% of this maximal value to avoid residual free bromine. Fluorescence was measured in 1 cm quartz cuvettes using a Spex 212 Fluorolog Spectrofluorimeter. Excitation and emission slits were used with nominal bandpass of 4.5 nm. Excitation was at 280 nm and emission was scanned from 300 to 360 nm. Background without toxin was subtracted from all reported values.
RESULTS Ah'D DISCUSSION Figure toxin. In
1 shows
20-25%
toxin
It
nm below
the
is
takes is
of
this
at
at
low
noted
above
pH. low pH.
pH is
that the
These
in
transition
In
toxin
without
shift
in
general,
the
behavior
that
without
gradual
for
some
of
toxin
At present
variability. 287
shows
a gradual
fluorescence
NaCl and at pH 5-5.5 from
the
nicked
preparations we do not
326 nm to
that of
of
intensity.
to a low
indicate
more
our
decreased
Amax
results
solutions
fluorescence
"transition"
reproducibly
pH.
of aqueous
as pH is
by a rapid
by a red
We find
in the
at pH 4-4.5
accompanied transition
drop
fluorescence
followed
similar.
be
in
occurs
place
fluorescence
constant
first,
of pH on fluorescence
is a marked
drop
The transition
mlf NaCl.
should
the
decrease
state.
toxin
effect
At low pH there
intact
change
the
in
about
150 333
a conformational nicked
NaCl
the
toxin.
and intact change
in
However,
it
fluorescence understand
the
is source
Vol. 120, No. 1, 1984
BIOCHEMICAL
AND BIOPHYSICAL RESEARCH COMMUNICATIONS
.6 -
.O i
.6 -
.8 -
OI
02
PH
I
I
I
I
50
I
I
150
IO0
O
[NCICI]
(mM)
Figure 1: Effect of pH upon Fluorescence of Diphtheria Toxin. (A) Intact toxin (4.5 pg/ml). (B) Nicked toxin 5.1 pg/ml. Samples contained toxin in 10 mM buffer with (-) or without (---) 150 mM NaCl. Na phosphate buffer was used at pH 2.3 and 6 to7; Na formate buffer at pH 3 to 4.5. Na acetate buffer was used at pH 5 and 5.5; tris-Cl buffer was used at pH 9. Samples were incubated lh before fluorescence at 33Onm was measured. Figure 2: Effect of NaCl upon Toxin Fluorescence at pH 5. Concentrated was added to a sample of 4.4 ug/ml intact toxin in 10 mM Na acetate Fluorescence was read 5 min. after each addition of salt. Figure
2 shows
gradually
stabilized
the
the
pH of Using
effect
of
binding
transition
brominated
is Brij
detergents,
which
detected
via
fluorescence As shown
as
of
the
Triton
and unbrominated
with
of
brominated
in figure
mild,
Brij
3, detergent
Brij
96 at
With
binding 288
of NaCl
this
each
method
pH.
that
appears
were
Detergent
with at
it
is
class
of
incubated binding
as the
ratio
unbrominated
pH 4-4.5
the
detergent
because
toxin
expressed to
present.
polyoxyethylene of
that
detergent
96 was chosen
Samples
is
implies
quenching
fluorescence, 96 relative
This
amount
non-ionic
X-100. Brij
tryptophan
exact
fluorescence
(5).
conformation
increased.
was examined.
detected
includes
quenching
a
fluorescent
is
to the
binding
member
weakly
concentration
96
can be conveniently
brominated
pH 5 the
sensitive
pH upon detergent
brominated
96.
at
as NaCl
an easily
with
that
NaCl 5.
pH
without
was of Brij NaCl
BIOCHEMICAL AND BIOPHYSICAL RESEARCH COMMUNICATIONS
Vol. 120, No. 1, 1984
0.4
F/FOE
‘Bi$-id
:
0.4 I 2
I 3
I 4
I 5
1 6
I 7
PH
of pH upon Quenching of Toxin Fluorescence by Br,,sinated Figure 3: Effect Detergent. (A) Intact Toxin (B) Nicked Toxin. Samples prepared as in figure 1 except that 0.1% (w/v) of either Brij 96 or dibrominated Brij 96 was present. Symbols same as Figure 1. Ordinate is the ratio of fluorescence in the presence of dihrominated Brij 96 (F) to that in the presence of Brij 96 (Fo).
and around appears
pH5 in is
15OmM NaCl.
close
transition.
to
It
associated
is
or
Therefore,
the
lower
than
slightly
probable
with
either
the
The pH of
4-4.5,
at
that
the
formation
pH at which the
pH of
transition
in
or exposure
detergent the
toxin
binding
fluorescence
conformation
of a hydrophobic
is
site
on the
protein.
close
to
ionic
conditions,
value
of pH 5 found
of
pH is
that
reported
hydrophobicity atoms
are
these
in
what
is attached
experiments
a much more 150 mM NaCl
the
toxin
tryptophan
residues
At low pH, the 150 mM NaCl
to the
are
stronger
could
that
either
appears
Triton
closer
it
sucrose
encounter
in
is
that
likely
exposed quenching involve
to
the
a difference 289
fraction
toxin
relative in
tryptophan
toxin bromine
conclusion the
of to
range
induced
another
region
The
endosomes.
quenching
of
similar
This
or
acid
the
very
method. pH.
the
is
under
lysosomes
chain
hydrophobic
of nicked
binding gradient
Because
hydrocarbon considerable
NaCl,
to physiological
significant.
a
without
X-100
laborious is
detergent's that
for
should
physiologically
is
binding
(4)
we now can conclude
Therefore,
Brij
previously
using
about
which
of
fluorescent the
intact exposure
micelles. toxin
in
or
the
Vol. 120, No. 1, 1984 amount
of
residues
bound
detergent.
come into
contact
Even
with
conformation of
the
BIOCHEMICAL
these is not
the
including
to
these
the
CRM 45
toxin,
receptor-binding is
to toxin
story
of
could
at
may also
free
affect
pH control
example,
exist
of
acids
of
the
neutral
the
various factors
or
with
pH
hydrophobicity.
forms
example, of
(9).
may
reduced
For
C-terminal
pH
ions,
in many other
ApUp
from
toxin
may affect
in hydrophobicity.
near
tryptophan
environmental
can
differ
amino
X-100
For
toxin
subunits,
that
variables
and other
the
likely
--in vivo.
transition.
missing
Triton
is
additional
potential
forms
it
precise
Several
separated
of
binds
lipids
Furthermore
Any
fragment,
membrane the
membrane
aisulfiae. mutant
case
hydrophobic
transition. monomer,
either
results,
a pH gradient,
affect
with
complete.
hydrophilic
lipids,
In
AND BIOPHYSICAL RESEARCH COMMUNICATIONS
its
B
Furthermore,
Clearly,
more work
needed. Fluorescence
lipids
has
several
protein
recently
aspects
brominated
quenching
of
detergents
been
by
introduced
lipid-protein will
spin-labeled as
(10,ll) a powerful
interaction
also
and
be a powerful
tool
(14). tool
This for
brominated for
(12,13)
elucidation
report
shows
of that
understanding
membrane
to E.L.,
19131
behavior. ACKNOWLEDGEMENTS
R.S.
This work was supported and a S.U.N.Y. University
by N.I.H. grant Award to E.L.
GM 31986
A.I.
to
REFERENCES 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. 13. 14.
Lenard, J. and Miller, D.K. (1982) Cell, 2, 5-6. Simon, M.I. and Draper, R.K. (1980) J. Cell Biol. 87, 849-854. Sandvig, K. and Olsnes, S. (1980) J. Cell. Biol. 3, 828-832. Sandvig, K. and Olsnes, S. (1981) J. Biol. Chem. 256, 9068-9076. London, E., Zhao, J.-M., Chattopadhyay, A., Blewitt, M., McKeever, B. and Sarma, R., Proceedings of the New York Academy of Sciences 1983 Colloquium in Biological Sciences, in press. McKeever, B. and Sarma, R. (1982) J. Biol. Chem. 257, 6923-6925. Barbieri, J.T., Carrol, S.F., Collier, R.J. and McCloskey, J.A (1981) J. Biol. Chem. e, 12247-12251. CRC Handbook of Biochemistry and Molecular Biology, Vol. 1 (1976)(G.D. Fasman ed.) CRC Press, Cleveland 552 pp. Boquet, P., Silverman, M.S., Pappenheimer, A.M. Jr. and Vernon, W.B. (1976) Proc. Nat. Acad. Sci USA 2, 4449-4453. London, E. and Feigenson, G.W. (1981) Biochemistry 3, 1939-1948. London, E. and Feigenson, G.W. (1981) Biochim. Biophys. Acta 649, 89-97. Leto, T.L., Roseman, M.A. and Holloway, P.W. (1980) Biochemistry E,1911-1916 East, J.M. and Lee, A.G. (1982) Biochemistry 21, 4144-4151. London, E., (1982) Molec. and Cell. Biochem. E, 181-188. 290