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Toxicology Letters, 56 (1991) 207-212
@ 1991 Elsevier Science Publishers B.V. (Biomedical Division) 0378-4274/91/$3.50
ADONIS037842749100067L
TOXLET 02550
Effects of triphenyltin acetate on pregnancy in rats by oral administration
Tsutomu Noda, Shigeru Morita, Tetsuo Yamano, Mitsuru Shimizu and Akio Yamada
Osaka City Institute of Public Health and Environmental Sciences, Osaka (Japan)
(Received 27 July 1990)
(Accepted 6 November 1990)
Key words: Triphenyltin acetate; TPTA; Embryotoxicity; Fetotoxicity
207
SUMMARY
A teratological test was carried out on triphenyltin acetate (TPTA) used as a fungicide and antifouling
agent. Pregnant Wistar rats were treated orally with TPTA at dose levels of 0, 1.5, 3.0, 6.0, 9.0 and 12.0
mg/kg/d during days 7-17 of gestation. Cesarean sections were performed on day 20 of gestation. In the
pregnant rats, 2 of 13 and 2 of 12 dams died at 9.0 and 12.0 mg/kg, respectively. Vaginal bleeding, bloody
mouth and nose, somnolence and depression of body weight gain and food intake were observed at 9.0
and 12.0 mg/kg at late stages of pregnancy. No statistically significant reductions in maternal thymus and
spleen weights were observed on day 20 of gestation. Increase in embryonic and fetal deaths and in dams
with total resorption of fetuses were observed at doses of more than 6.0 mg/kg. The doses of TPTA in
this experiment, however, induced no teratogenic effects in rats.
INTRODUCTION
Triphenyltin compounds have been widely used as biocides in marine antifouling paints and they are still important agricultural fungicides due to their specific activi- ties [l]. Triphenyltin compounds have chemosterile properties in insects, such as house flies (Musea domestica), German cockroaches (Blatella germanica), flour bee- tles (Tribolium confusum) etc. [2]. Triphenyltin acetate (TPTA) and triphenyltin chlo- ride produce degenerative changes in testicular tissues [3] and also produce significant
Address for correspondence: Tsutomu Noda, Osaka City Institute of Public Health and Environmental
Sciences, 8-34 Tojo-cho, Tennoji-ku, Osaka 543, Japan
208
changes in ovarian tissues including a decreased number of mature follicles, and an
increased incidence of atresia in early follicle growth in rats [4].
As regards mammalian teratogenic studies of triphenyltin compounds, two studies
have been published in which TPTA [5] and triphenyltin hydroxide [6] were shown
to have no teratogenicity in rats. But in the study of TPTA, the chemical was admin-
istered to pregnant females on days 5-14 of gestation and maternal body weight on
day 5 of gestation was used for calculation of the doses. Thus the doses became re-
latively low at the end of the treatment period because the animals underwent a more
than 15% increase in body weight during that period. In the present study, we re-
evaluated the teratogenic potential of triphenyltin acetate (TPTA) in rats treated
orally during the organogenetic phase of gestation (days 7-l 7).
MATERIALS AND METHODS
TPTA was purchased from Wako Pure Chemical Industries, Ltd. (Osaka, Japan).
Four-week-old Wistar rats of both sexes (CLEA Japan, Inc., Tokyo, Japan) were
individually housed in a room with a constant day/night cycle (dark period from 7:00
p.m. to 7:00 a.m.) at 23 f 2°C temperature and 60 f 10 % relative humidity. They were
given feed (NMF, Oriental Yeast Co., Ltd., Tokyo, Japan) and tap water ad libitum.
A 3-month-old female rat was paired overnight with a male of the same age, and
the day on which sperm was observed in the vaginal smears was designated as day
0 of gestation. Mated females were randomly assigned to 6 groups (13-14/group).
TPTA was dissolved in olive oil and administered to females by stomach tube at
doses of 0, 1.5, 3.0, 6.0, 9.0 and 12.0 mg/kg during days 7-17 of gestation. The vol-
ume of vehicle was held constantly at 2 ml/kg of maternal body weight. Control ani-
mals were administered an appropriate volume of vehicle without TPTA.
Every day, body weight and food consumption were measured and general behav-
ior was observed. All females were euthanized under ether anesthesia on day 20 of
gestation. Upon laparotomy, the position and number of live and dead fetuses in-
cluding resorbed fetuses in the uterus were recorded. The number of corpora lutea
and maternal thymus and spleen weights were also recorded. A uterus with total re-
sorption was isolated and stained with 10 % ammonium sulfide to determine the total
number of implantations. Live fetuses were weighted and examined for their sex and
external malformations. One-half of the live fetuses in each litter was fixed in 95%
ethanol and processed for staining of the skeletons for skeletal abnormalities by the
alizarin red S dye method [7]. The other half was fixed in Bouin’s solution and exam-
ined for visceral abnormalities according to the method of Wilson [S].
Data were analyzed by Dunnett’s [9] or Scheffe’s [lo] multiple comparison method
in a parametric or non-parametric manner. Data were analyzed in the groups which
received doses up to 9.0 mg/kg because there was only one pregnant animal with live
fetuses in the highest dose group (12.0 mg/kg).
209
RESULTS
Oral treatment of pregnant rats with TPTA during the organogenetic phase of ges-
tation caused maternal death and reduction of maternal body weight gain and food
intake at 9.0 and 12.0 mg/kg (data not shown). Two pregnant animals with vaginal
bleeding at 9.0 and 12.0 mg/kg, respectively, died during day 9-13 of gestation. Ani-
mals receiving 6.0 mg/kg or more showed piloerection. Vaginal bleeding, somnolence
and bloody mouth and nose were observed in about half of the animals at 9.0 mg/kg
and almost all at 12.0 mg/kg. However, no toxic signs were seen at doses up to 3.0
mg/kg. Maternal thymus weights seemed to be reduced at 9.0 mg/kg, although this
was not statistically significant, whereas maternal spleen weights were not reduced
at the same dose level (Table I).
Total resorption of fetuses was observed in 2/13 litters at 6.0 mg/kg, 6/l 1 at 9.0
mg/kg, and S/l0 at 12.0 mg/kg. Even in the dams with live fetuses, the rate of resorp-
tion increased at late stages of gestation at 9.0 mg/kg. The number of live fetuses
and the mean fetal body weights of both sexes seemed to decrease at 9.0 and 12.0
mg/kg, although the number of implants and the sex ratio were unaffected (Table
II). When data were calculated for all the pregnant animals including those with total
resorption, the rates of resorption in the groups treated with TPTA at 6.0, 9.0 and
12.0 mg/kg were 21.4, 60.8 and 97.3% (P~0.01) at an early stage of gestation, and
1.6, 11,9 and 1.3% at late stages of gestation, respectively, while the mean numbers
of live fetuses were 10.4 f 4.84, 4.2 f 5.74 and 0.2 f 0.63 (P-C 0.0 l), respectively.
From external and visceral observations, the incidence of fetuses with malforma-
tions did not increase in the TPTA-treated groups. Also from the skeletal observa-
tions, no significant increase in malformations was found in the fetuses in the treated
groups. Minor skeletal variations, such as cervical rib and rudimentary lumbar rib
(less than half the length of 13th rib [ 111) did not increase in the fetuses in the treated
groups. The number of sternebrae and proximal and middle phalanges of the hind-
limbs as an index of the degree of ossification decreased in the fetuses from dams that
received 9.0 mg/kg (Table III).
DISCUSSION
Snoeij et al. [12] have reported that triphenyltin chloride induced a dose-related
reduction of thymus and spleen weights in rats fed at dietary concentrations of 15,
50 and 150 ppm for 2 weeks. A reduction in spleen weight was also observed upon
feeding triphenyltin compounds [13]. In the present study, however, the thymus and
spleen weights of pregnant rats treated orally with TPTA at dose levels of 1.5, 3.0,
6.0, 9.0 and 12.0 mg/kg from days 7-17 of gestation were not reduced significantly.
Even when data were calculated for all the pregnant animals including those with
total resorption of fetuses (2 at 6.0 mg/kg, 6 at 9.0 mg/kg and 9 at 12.0 mg/kg), no
significant reductions were observed in these organ weights.
TA
BL
E
I
EFF
EC
TS
OF
TPT
A
ON
MA
TE
RN
AL
SP
LE
EN
A
ND
T
HY
MU
S W
EIG
HT
S 3
_-._
-_
- --
-.
0
Oliv
e oi
l T
PTA
@
g/kg
) (2
ml/k
g)
1.5
3.0
6.0
9.0
12.0
n 14
13
12
II
5
1 B
ody
wt.
(8)
314k
l2.1
32
8 5
24.9
31
4k19
.2
303
+- 2
5.7
288i
38
.0
228
Sple
en w
t. (m
g)
591*
31.5
62
2 f
69.4
56
2k45
.4
546h
67.4
52
3& 1
26.3
405
Thy
mus
w
t. (m
g)
174+
15.7
19
9k37
.1
188
+ 2
7.9
153k
66.7
16
+
372
73
Val
ues
are
the
mea
n +
sta
ndar
d de
viat
ion.
Tw
o da
ms
(6.0
mg/
kg),
6
dam
s (9
.0 m
g/kg
) an
d 9
dam
s (1
2.0
mg/
kg)
with
tot
al
reso
rptio
ns
are
excl
uded
fr
om
thes
e da
ta.
TA
BL
E
II
EFF
EC
TS
OF
TPT
A
ON
TH
E
PRE
GN
AN
T
RA
TS,
L
ITT
ER
S A
ND
FE
TU
SES
AFT
ER
T
RE
AT
ME
NT
O
F PR
EG
NA
NT
R
AT
S
Oliv
e 01
1 fP
TA
(w/W
(2
ml/k
g)
1.5
3.0
6.0
9.0
12.0
-.
No.
of
fem
ales
in
sem
inat
ed
14
13
13
13
13
13
No.
of
preg
nant
fe
mal
es
14
13
12
13
13
12
No.
of
dam
s w
ith l
ive
fetu
ses
14
13
12
11
5**
I**
No.
of
dam
s w
ith t
otal
re
sorp
tion
0 0
0 2
b**
9**
No.
of
dead
dam
s 0
0
0
0
2 2
No.
of
corp
ora
lute
a a.
b 14
.3*0
.73
15.4
+
1.94
14
.7+
1.
97
14.8
22.6
4 l&
2+2.
59*
IS.0
N
o. o
f im
plan
tvb
13.6
rtO
.93
14.2
kO.9
9 13
.5+
2.15
13
.5rt
: 1.
51
15.6
kO.8
9 15
.0
Inci
denc
e of
dea
d or
res
orbe
d fe
tuse
s (s
)~
Ear
ly
stag
e 5.
9 4.
3 7.
5 7.
1 13
.8
73.3
L
ate
stag
e 0
0.5
0.8
1.9
26.3
**
13.3
N
o. o
f liv
e fe
tuse
sa
12.9
k1.2
3 13
.5+
1.2
7 12
.422
.47
12.3
Lt: 1.62
9.2k
4.97
2.
0 Se
x ra
tio
(M/F
) 1.
1(86
/94)
1.
0(83
/93)
1.
2(78
:71)
1.
5(75
/M))
1.
7(25
/21)
I.o
(l:l)
B
ody
wei
ght
of l
ive
fetu
sesa
(g)
M
ale
3.2k
O.2
7 3.
3iO
.18
3.4
+ 0
.49
3.2~
0.11
2.
3 20
.47
1.5
Fem
ale
3.0*
0.17
3.
liO.1
4 3.
2+0.
52
3.0&
0.16
2.
1 io
.52
1.9
~___
__
_-__
a Val
ues
are
the
mea
n f
stan
dard
de
viat
ion.
hT~o
da
ms
(6.0
mgi
kg),
6 d
ams
(9.0
mg/
kg)
and
9 da
ms
(12.
0 m
g/kg
) w
ith t
otal
re
sorp
tions
ar
e ex
clud
ed
from
th
ese
data
.
l S
igni
fica
ntly
di
ffer
ent
from
con
trol
s,
P<
0.
05.
**Si
gnif
ican
tly
diff
eren
t fr
om c
ontr
ols.
P
<O
.Ol.
The
litt
er
was
use
d as
the
sta
tistic
al
unit
for
calc
ulat
ion
of f
etal
va
lues
. T
hus
thes
e va
lues
re
pres
ent
the
mea
ns
of l
itter
m
eans
w
ithin
ea
ch g
roup
.
TA
BL
E
111
EX
TE
RN
AL
, V
ISC
ER
AL
A
ND
SK
EL
ET
AL
O
BSE
RV
AT
ION
S O
F FE
TU
SES
FRO
M
DA
MS
TR
EA
TE
D
OR
AL
LY
W
ITH
T
PTA
Ext
erna
l ob
serv
atto
ns
No.
of
fetu
ses
exam
ined
Inct
denc
e of
fet
uses
with
mal
form
atio
ns
(%)
No.
of
fetu
ses
with
mal
form
atio
ns
Ves
tigia
l ta
il
Vis
cera
l ob
serv
atio
ns
No.
of
fetu
ses
exam
rned
Inci
denc
e of
fet
uses
with
mal
form
atio
ns
(%)
Skel
etal
ob
serv
atio
ns
No.
of
fetu
ses
exam
ined
Inci
denc
e of
fet
uses
w
ith m
alfo
rmat
ions
(%
)
No.
of
fetu
ses
wtth
mal
form
atio
ns
Age
nesi
s of
the
coc
cyge
al
vert
ebra
e In
cide
nce
of f
etus
es w
th
vari
atio
ns
(F)
No.
of
fetu
ses
with
var
iata
ons
Occ
ipita
l hy
popl
asia
Cer
vica
l ri
b
Split
ting
of 1
st c
ervi
cal
vert
ebra
l ar
ch
Shor
teni
ng
of 1
3th
rib
Rud
imen
tary
lu
mba
r ri
bs
Var
iatio
ns
in n
umbe
r of
lum
bar
vert
ebra
e
Deg
ree
of o
ssif
icat
iona
No.
of
ster
nebr
ae
No.
of
prox
imal
an
d m
tddl
e ph
alan
ges
Fore
hmb
Hin
dlim
b
No.
of
sacr
al
and
caud
al
vert
ebra
e
Oliv
e oi
l
(2 m
l/kg)
P
TA
(w
/W
I.5
3.0
6.0
9.0
12.0
I80
176
149
I35
46
2
0 O
.S( I
) 0
0 0
0
0 l(
l)
0 0
0 0
83
81
68
62
22
0
0 0
0 0
0 0
97
95
81
73
24
0 1.
0(l)
0
0 0
0 l(
l)
0 0
0
7.2(
5)
1.1(
l)
6.1(
3)
14.1
(7)
I I .4
(2)
0 0
0 0
0
6(5)
l(
l)
2(2)
8(
5)
3(2)
l(
l)
0 0
2(I)
0
0 0
0 0
l(l)
0
0 0
l(l)
0
0 0
2(2)
0
2(l)
0 50.q
I)
l(l)
0 0 0 0 l(
l)
4.3*
0.41
4.
8&0.
44
5. I
f0.4
2”
4.7k
O.3
5 3.
1 kO
.92’
. 2.
0
4.0
* 0.
84
5.2k
O.6
3 5.
5*
1.00
’ 5.
7*0.
26**
3.
9+
1.03
4.
0 *
0.00
4.
0 *
0.00
4.
3*1.
10
4.0~
0.00
3.
6 k
0.44
.’
6.9+
0.36
7.
1+0.
36
7.3k
O.5
8 7.
1 kO
.23
5.7k
O.7
8
3.0
3.5
5.0
‘Val
ues
are
the
mea
nt
stan
dard
de
wat
ion.
( ) N
o. o
f co
ncei
ved
mot
hers
w
ith c
ase
*Sig
nifi
cant
ly
difT
eren
t fr
om c
ontr
ols,
P
< 0
.05.
**Si
gnif
ican
tly
diff
eren
t fr
om c
ontr
ols.
P
cO.0
1.
The
litt
er
was
use
d as
the
sta
tistic
al
unit
for
calc
ulat
ton
of f
etal
val
ues.
T
hus
thes
e va
lues
re
pres
ent
the
mea
ns
of l
itter
m
eans
w
ithm
ea
ch g
roup
212
No embryotoxic and fetotoxic effects of TPTA were observed at less than 3.0 mg/
kg, although the number of dams with total resorption of fetuses in a dose-dependent
manner at more than 6.0 mg/kg. Moreover, TPTA at 9.0 and 12.0 mg/kg seemed
to increase post-implantation loss and to decrease the body weights of live fetuses
and the incidence of bleeding in the uteri. Giavini et al. [5] have reported that 4 of
10 pregnant females which received TPTA orally at 15 mg/kg on days 5-14 of gesta-
tion showed total resorption of fetuses, but not at up to 10 mg/kg. They used mater-
nal weight on day 5 of gestation to calculate the doses, but since we used daily mater-
nal weight for this, our total dosage of TPTA to a pregnant female was greater than
theirs.
No malformations were found upon external, visceral and skeletal observation in
fetuses from dams treated orally with TPTA during the organogenetic phase of gesta-
tion even at dose levels exhibiting obvious maternal toxicity. The present study sug-
gests that TPTA is not teratogenic, but that it is harmful to pregnant rats.
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