Ch~most,here, W~1.10, ~o.7, pp 779 - 793, 1 9 5 l Printed in Great Britain
DIFFERENCES
0045-6535/91/070779-07~02.00/O ©1981 Pergamon Press Ltd.
IN THE B I O T R A N S F O R M A T I O N IN MALE AND FEMALE
E.Richter,
Institut Medizinische
G.Renner,
and M.Wick
und Toxikologie,
der L u d w i g s - M a x i m i l i a n s - U n i v e r s i t ~ t
D-8000
MGnchen
(HCB)
RATS
J.Bayerl,
fGr P h a r m a k o l o g i e
Fakult~t
NuSbaumstr.26,
OF H E X A C H L O R O B E N Z E N E
2, Federal
Republic
MUnchen,
of Germany
ABSTRACT I. Male and female 770 mg HCB/kg spleen
Sprague-Dawley
body weight.
rats were given orally within one month
Livers and pooled
and heart were analysed
samples
of kidneys,
3, 24 and 52 days after
the last dose
for HCB and its m e t a b o l i t e s . 2. P e n t a c h l o r o p h e n o l
(PCP),
pentachlorothiophenol
2,3,5,6-tetrachlorophenol found besides 3. There
exists
HCB in all organs a significant
livers
of male and female
higher
content
Also
decreased
PCTP c o n c e n t r a t i o n s
No marked
difference rats,
decrease
2,3,4,6-
and
(PCB) were
investigated. in the metabolite
mainly attributed
of PCTP in females
4. HCB c o n c e n t r a t i o n s
(PCTP),
(TCP) and p e n t a c h l o r o b e n z e n e
pattern
in
to a significantly
than in males.
slower
decreased
in female slower
than in male rat livers.
in females
than in males.
at all was found during 7 weeks of elimination
in
females. 5. Differences explanation and
female
in the b i o t r a n s f o r m a t i o n for the different
of HCB could
porphyrinogenic
rats.
779
thus be an
activity
of HCB in male
780
INTRODUCTION
Hexachlorobenzene its m a j o r
(HCB) is a w i d e s p r e a d
toxic effects
r e s e m b l i n g p o r p h y r i a cutanea f r e q u e n t l y as chemical genesis
environmental
is to cause a chronic tarda in man.2'3
inducer in animal
of p o r p h y r i a cutanea
a c t i o n of HCB, however,
was found. 5,6
HCB has been used
to e l u c i d a t e
the patho-
In addition,
in the m e t a b o l i t e
of
in rat studies a marked sex
to male rats.
female rats after s u b c h r o n i c
A c c o r d i n g to Koss et al.4
of HCB is a p r e r e q u i s i t e
Female rats d e v e l o p e d
lower doses of HCB as c o m p a r e d
sex d i f f e r e n c e
is closely
tarda. The m e c h a n i s m of the p o r p h y r i n o g e n i c
is still not u n d e r s t o o d .
i n d u c t i o n of the porphyria.
of male and
Therefore
studies
it seems very likely that b i o t r a n s f o r m a t i o n
difference
pollutant. I One of
p o r p h y r i a which
porphyria
earlier and at
T h e r e f o r e we a n a l y s e d
HCB a d m i n i s t r a t i o n
livers
to look for a
pattern.
M A T E R I A L S AND M E T H O D S
Animals
Male and female S p r a g u e - D a w l e y F.R.G.)
of about
commercial
rats
(Versuchstierzucht
300 and 260 g body weight,
rat diet
(Altromin,
Lage,
Wiga,
respectively,
F.R.G.)
Sulzfeld,
were given a
and water ad libitum.
Materials
Hexachlorobenzene
and its m e t a b o l i t e s
2 , 3 , 5 , 6 - T C P were purified by g.l.c..
PCB,
PCP,
by r e c r y s t a l l i z a ~ i o n .
PCTP,
2,3,4,6- and
Purity of HCB was >99,7 %
Anisoles and t h i o a n i s o l e s were p r e p a r e d by m e t h y l a t i o n of the
c o r r e s p o n d i n g phenols and t h i o p h e n o l s with d i a z o m e t h a n e .
Methods
Each 40 male and female rats were given orally w i t h i n one month nine doses of 0.3 m m o l l k g
(85.6 mglkg)
of h e x a c h l o r o b e n z e n e
arachis oil in time intervals of 3 or 4 days. received
killed.
30 H C B - t r e a t e d
Body weight was r e c o r d e d weekly.
blood was c o l l e c t e d tocrit tubes, 7
hemoglobin.
24 and 52 days after the
At the end of the e x p e r i m e n t
for d e t e r m i n a t i o n of packed
Clay Adams,
Three days after the
rats of each sex and all control rats were
Five male and female rats were killed
last dose.
in
Ten rats of each sex
arachis oil only and served as control.
last dose
dissolved
Parsippany,
Liver, kidney,
cell volume
(Micro-hema-
USA) and c o n c e n t r a t i o n of
heart and spleen were dissected,
and frozen at -20 °C until analysis.
weighed,
781
D e t e r m i n a t i o n of h e x a c h l o r o b e n z e n e
Whole
and its m e t a b o l i t e s
livers and pooled samples of kidney,
spleen and heart were
t h o u r o u g h l y ground with sea sand in a mortar, 0.1M
HCI and subjected
n-hexane
as solvent
treated with 500 ml of
to a s t e a m - d i s t i l l a t i o n - e x t r a c t i o n
for three hours.8
of HCB and its major metabolites,
(SDE) with
Under these conditions
chlorinated
benzenes,
recoveries
phenols and thio-
phenols were almost complete. The hexane extract was dried over sodium sulfate,
concentrated
nitrogen
Excess d i a z o m e t h a n e was
and treated with d i a z o m e t h a n e
removed with nitrogen. concentrated
The hexane was
pilot
coupled with a Varian
and by capillary gas c h r o m a t o g r a p h y study the amounts of m e t h y l a t e d
T h e r e f o r e no d i f f e r e n t i a t i o n
g.l.c°-m.s.
1700 gas c h r o m a t o -
(Fraktovap,
Carlo Erba).
phenols and thiophenols
he×ane extract after the SDE p r o c e d u r e was estimated. a n i s o l e s and only minor amounts
In a
in the
No c h l o r i n a t e d
of p e n t a c h l o r o t h i o a n i s o l e
between
under
further cleaned up by shaking with
sulfuric acid and a n a l y s e d by g.l.c.-e.c.,
(Varian CH5 mass s p e c t r o m e t e r graph)
in hexane.
were
found.
free phenols and t h i o p h e n o l s and the
c o r r e s p o n d i n g anisoles and t h i o a n i s o l e s was made.
C a l c u l a t i o n s were
based on the free phenols and thiophenols.
Statistics
For c o m p a r i s o n of m e t a b o l i c multifactorial
analysis
4004/151.
Statistical
Student's
t test.
patterns
in livers of male and female rats a
of variance was c a l c u l a t e d with a Siemens
e v a l u a t i o n of sample means was made by a two tailed
RESULTS
One female rat died during the seventh week after the last dose of HCB. No s i g n i f i c a n t relative
d i f f e r e n c e s were seen in body weight gain and a b s o l u t e and
(to body weight)
weight was c o n s i d e r a b l y
w e i g h t s of kidney,
increased
heart and spleen.
Liver
three days after the last HCB dose from
7 . 1 8 ± 1 . 4 7 g (2.34±0.36 % of body weight)
to 13.02±2.15 g (4.34±0.73 %) in
male rats and from 5 . 7 8 ± 0 . 5 4 g (2.40±0.20 %) to 7.60±1.74 g (3.13±0.60 %) in female
rats.
Packed cell volumes were s i g n i f i c a n t l y
54.3±2.4 % to 5 2 . 1 ± 3 . 1 % in female rats. different
reduced
from
in male rats and from 47.6±1.8 % to 44.6±3.0 %
C o n c e n t r a t i o n of h e m o g l o b i n was not s i g n i f i c a n t l y
between treated and u n t r e a t e d groups.
782
Table
I.
Concentration of HCB and its metabolites
in the tissues of
male and female rats after oral administration of 0.3 mmol/kg HCB dissolved
in oil every 3 to 4 days.
are given as mean and standard deviation heart and spleen.
Results
(x±s x) in the case of
liver and as single value of pooled samples kidney,
of nine doses
in the case of
Values are expressed as mg/kg tissue
(wet weight)
day sex
n
HCB
PCB
PCP
PCTP
TCP
liver 3
24
52
m
30
192.2±70.2
0.048±0.017
3.16±1.70
0.234±0.087
0.017±0.012
f
30
147.0±72.5
0.033±0.014
2.12±1.66
0.356±0.123
0.041±0.051
m
5
37.2±5.4
0.011±0.008
0.34±0.10
0.166±0.060
0.007±0.007
f
5
72.4±13.4
0.007±0.001
0.76±0.46
0.268±0.059
0.012±0.009
m
5
30.7±12.4
0.011±0.004
0.52±0.32
0.116±0.043
0.010±0.006
f
4
58.4±10.6
0.009±0.002
0.47±0.25
0.373±0.078
0.011±0.010
kidney 3
m
30
127.4
0.045
5.792
0.242
0.089
f
30
111.4
0.012
3.690
0.098
0.075
24/52 m
l0
32.1
0.006
0.488
0.161
0.006
f
9
47.5
0.008
0.254
0.061
0.018
heart 3/24/52
m
40
62.9
0.004
0.690
0.036
0.075
f
39
80.5
0.005
0.640
0.018
0.010
0.591
0.098
0.007
spleen 3/24/52
m
40
f .
.
.
.
.
.
.
.
.
.
.
.
64.7
39 .
.
.
.
Significantly
0.006
67.1 .
.
.
.
.
.
.
.
0.011 .
.
.
different
.
.
.
.
.
.
.
.
.
.
.
0.244 .
.
.
.
.
.
.
.
.
.
.
.
.
.
.
.
from the corresponding
0.038 .
.
.
.
.
.
.
.
.
.
.
.
.
.
0.009 .
.
.
.
.
value for male rats p<0.05
7~3
The results of the q u a n t i t a t i v e in liver,
kidney,
determination
of HCB and its m e t a b o l i t e s
heart and spleen are s u m m a r i z e d
in table
I. Three days
after the last dose livers of male rats c o n t a i n e d s i g n i f i c a n t l y more HCB, PCB and PCP, but s i g n i f i c a n t l y rat livers.
less PCTP and TCP as compared to female
After 24 and 52 days
female rat livers had s i g n i f i c a n t l y
higher HCB and PCTP c o n c e n t r a t i o n s a n a l y s i s of pooled samples not be s t a t i s t i c a l l y
evaluated.
PCTP in these organs were rats.
A multifactorial
analysis
24 days after the last dose
In contrast
pattern
concentrations
(table 3).
Table 2.
analysis
HCB and its m e t a b o l i t e s
of
in female compared to male confirmed
the s t a t i s t i c a l l y
in male and female livers
(table 2). A c o r r e l a t i o n analysis
and between HCB and PCTP
Because of
heart and spleen could
to liver,
of v a r i a n c e
showed a s i g n i f i c a n t
Multifactorial
for kidney,
in no case higher
significant different metabolic
all m e t a b o l i t e s
as the livers of male rats.
the results
3 and
for HCB and
c o r r e l a t i o n only between HCB and PCP
of v a r i a n c e PCB,
PCP,
for the c o n c e n t r a t i o n s
PCTP and TCP between
of
livers
of male and female rats.
Days after
Number and sex
Degrees of
of animals
freedom
last dose
3
30 m a l e / 3 0
female
T-value
Significance
5154
20.556
p < 0.01
24
5 male/5
female
5/4
28.715
p < 0.01
52
5 male/4
female
513
4.985
p > 0.05
The presence of p e n t a c h l o r o b e n z e n e
and the m e t h y l a t i o n
c h l o r o p h e n o l and p e n t a c ~ l o r o t h i o p h e n o l , chlorothioanisole confirmed
pentachloroanisole
and penta-
in hexane e x t r a c t s of organs was q u a l i t a t i v e l y
by g.l.c.-m.s.
g.l.c.-m.s.
products of penta-
The amount of t e t r a c h l o r o a n i s o l e was to low for
In c a p i l l a r y gas c h r o m a t o g r a m s
2,3,4,6- and 2 , 3 , 5 , 6 - t e t r a c h l o r o a n i s o l e ,
peaks of both isomers,
were
found.
784
Table
3.
Linear r e g r e s s i o n a n a l y s i s
between HCB and its m e t a b o l i t e s
PCP and PCTP in livers of male and female rats
3 days after
the last dose.
Metabolite
Sex
Intercept
Slope
Correlation
Significance
coefficient
PCP
male
- 0.217
0.0178
0.755
p < 0.001
female
- 0.071
0.0155
0.698
p < 0.001
PCTP
male
0.0779
0.000813
0.654
p <0.001
female
0.2413
0.000782
0.461
p <0.05
DISCUSSION
After rats were r e p e a t e d l y treated with h e x a c h l o r o b e n z e n e females c o n t a i n e d of males.
s i g n i f i c a n t l y more p e n t a c h l o r o t h i o p h e n o l
Our e x p e r i m e n t s
the livers of than the livers
did not allow a d e c i s i o n as to wether a higher
rate of p r o d u c t i o n or a lower rate of e l i m i n a t i o n was the cause difference.
Pentachlorothiophenol
derivatives
are known as HCB m e t a b o l i t e s .
the g l u t a t h i o n e metabolite.9 thiophenol,
c o n j u g a t e of HCB,
for this
and some other s u l f u r - c o n t a i n i n g They a p p a r e n t l y
originated
from
its primary s u l f u r - c o n t a i n i n g
Although various m e t a b o l i t e s
of HCB,
including pentachloro-
o b v i o u s l y did not lead to the same d i s t u r b a n c e
in the
p o r p h y r i n m e t a b o l i s m as HCB by itself~01 other still unknown reactive intermediates metabolites, philic
of HCB degradation, could be responsible.
respectively
r e a c t i o n p r o d u c t s of its
Such s u b s t a n c e s
should have electro-
sites which e v e n t u a l l y could react with
sulfhydryl
groups of the u r o p o r p h y r i n o g e n
the n u c l e o p h i l i c 4 decarboxylase. The d i s t u r b a n c e
of the p o r p h y r i n pathway by HCB is mainly a t t r i b u t e d
to a d e c r e a s e
in the
a c t i v i t y of this enzyme. 3 A higher c o n c e n t r a t i o n of p e n t a c h l o r o t h i o p h e n o l and t h e r e f o r e of possible livers of female susceptibility
reactive
intermediates
of HCB m e t a b o l i s m in
rats could p o s s i b l y be an e x p l a n a t i o n
of female rats to the p o r p h y r i n o g e n i c
for the higher
a c t i o n of HCB.
ACKNOWLEDGEMENTS
The a u t h o r s are g r a t e f u l
to the funds of C.Bohnewand,
T . G r a v e n h o r s t and K . L . W e i g a n d
for their support.
E.Hauber,
G. and
7a5
REFERENCES
I. 2.
Courtney,K.D., De Matteis,F.,
Environ. Res. 20, 225 (1979) Prior,B.E. and Rimington,C.,
3.
Elder,G.H.,
4.
(1976) Koss,G.,
5.
Int.J.Biochem. 12, 1003 (1980) Ippen,H., Aust,D. and Goerz,G.,
6.
Grant,
78. 9. 10.
Toxicol. 14, 422 (1975) Kiese,M., Arch. Exp. Path. Pharmakol. 235, 354 (1959) Renner,G., Richter,E. and Schuster,K.P., Chemosphere ~, 669 (1978) Renner,G., Richter,E. and Schuster,K.P., Chemosphere ~, 663 (1978) Koss,G., Koransky,W. and Steinbach,K., Arch.Toxicol. 42, 19 (1979)
Evans,J.O.
Seubert,S.,
and Matlin,S.A.,
Seubert,A.,
D.L., Shields,J.B.
Nature
Koransky,W.,
51, 71
Kraus,P. and Ippen,H.
Arch. Dermatol.Forsch.
and Villeneuve,D.C.,
(Received in Germany 2g ADril 195i)
191, 363 (1961)
Clin.Sci.Mol.Med.
245, 305 (1972)
Bull.Environ. Contam.