Degradation of p32-Bromophosby Microorganisms and Seedlings By J. STENERSEN Norwegian Plant Protection Institute, VoIlebekk, Norway Biological degradation of bromophos has been studied by Rowlands (i) and Stiansi et al. (2).
They
conclude that among other products desmethylbromophos (mbPS) is formed in wheat grains and rats.
No bis-
desmethyl bromophos (bPS) was found in their studies. This paper describes the degradation of p32_ bromophos by microorganisms and some seedlings, using qualitative thin layer chromatography to detect the products. METHODS Materials p32-1abeled bromophos was commersially obtained from Amersham radiochemical centre, U.K.
The compound
was purified by elution through a column of activated silica gel by tetrachlorcarbon 0
Unlabeled bromophos
and methyl parathion were obtained as gifts from producers os these insecticides.
Methyl phenyl phos-
phorothionate
(m~PS) and sodium hydrogen phenyl phos-
phorothionate
(~PS) w e r e s y n t h e t i s e d
in o u r
laboratory.
The p o t a s s u m s a l t
as a gift
from Dr.
Princeton,
U.S.A.
tained
as a gift
Sutherland,
converted
u n d Sohn C h e m i s c h e F a b r i k ,
o f bPS c o u l d
determined.
The s p o t s ,
reaction
ing sprays. that
obtained
stable
n o t be d i r e c t l y
t o be bPS, and
was e x a c t l y
gave
phenyl
the
was u s e d a s t h e
was h i g h e r
DPS h a s a h i g h e r rather
therefore
detect-
same a s
w i t h ~PS when DQC ( 2 . 6 - d i b r o m o b e n z o e -
quinone-4-chloroimide) The RF v a l u e
Germany.
o f bPS was o b t a i n e d .
phosphate-
The c o l o u r
The
from C.H. B o e h r i n g e r
supposed
with
t o mPS.
Ingelheim,
substance
The i d e n t i t y
positive
o f m2PS, o b -
f r o m B a y e r C h e m i e AG, L e v e r k u s e n ,
o f mbPS was a g i f t
No r e f e r e n c e
C y a n a m i d e Company,
The ammonium s a l t
G e r m a n y , was s p o n t a n i o u s l y sodium salt
o f m2PS was o b t a i n e d
value
against
compound g a v e p r o d u c t s
than than
alkali,
the
spray
value
mDPS.
for
reagent.
mbPS, a s
A l t h o u g h mbPS i s
hydrolysis
w i t h RF v a l u e s
of this
and colour
r e a c t i o n s with DQC identical w i t h mPS and bPS. A s o l u t i o n of m2PS, mbPS and bromophos nol was found after several weeks,
in etha-
to contain two
more substances w h i c h was c h r o m a t o g r a p h i c a l l y tified as mPS and bPS.
iden-
This s o l u t i o n was u s e d as
r e f e r e n c e s o l u t i o n throughout the study.
105
Analysis Analysis
of the incubation mixture were done
by thin layer chromatography.
Activated silica
gel G layers with the thickness
0.5 mm or 0.25 mm
were used.
The chromatograms
were developed
in
acetonitril
: water
p32-1abeled
compounds were located on the chromato-
(85 : 15) or (80 : 20) v/v
(3).
gram by laying an X-ray film in close contact with the plate for 24 hours.
The reference substances
were localised by spraying with the DQC reagent (1% 2.6-dibromobenzoequinone-4-chlorimide acid).
This reagent
phosphorothionates
(3)
in acetic
gives red colours with aryl
(aPS), and m2PS, and yellow
colours with maPS and mPS. Microbiological
studies
Preliminary
studies with the fungi Alternaria
tenius and Trichoderma
li~norum had shown that all
the water solublemetabolites The mycel contained
were in the medium.
most of the unmetabolised
phos which was absorbed or adsorbed, soluble metabolite was detected. were macerated
but no water
After the myceles
in a mortar with quartz sand and
partioned between petrolether radioactivity
bromo-
and water,
all the
was found in the petrolether
106
phase.
Therefore
only the
medium was a n a l y s e d
in these
investigations. 50 strains of microorganisms from garden soil. extract agar
were isolated
They were isolated on soil
(4) (which contained
15 g agar,
1.0 g
glucose 0.5 g K2HPO 4, I00 ml soll extract and 900 ml water) with
and were grown in I ml of the same medium
no a g a r
added.
48 h o u r s
p32bromophos,
dissolved
48 h o u r s
after
the
solution
was a d d e d i n s u f f i c i e n t
a concentration the
medium.
the
in ethanol
of the
inoculation,
was a d d e d .
bromophos addition,
of 5 ~g/25
25 ~ 1
after
the
amounts to give
~1 of
its
compounds i n
medium was t h e n
on c h r o m a t o g r a m s o f 0 . 5 m m
standard
thickness
applied
and developed
as described. Laboratory Trichoderma solani the
strains
lignorum,
and Phizopus
Aspergillus
nigricans
tenius,
niger,
were also
Fusarium tested
using
same m e d i u m .
Studies
on s e e d l i n g s
Seeds of onion, with
of Alternaria
carrot
and wheat were treated
1 ~1 p32-bromophos solution
on a m o i s t e n e d
filter
paper.
107
pr.
seed and placed
A forthnight
after
the
treatment,
separated tely
the
roots,
and the
leaves
from the
seeds,
and the
parts
macerated
extracted solution already
quartz
in ethanol, added. described.
unmetabolised with
with
were separa-
in a mortar,
with
and then
some o f t h e
The e x t r a c t s I n s om e o f
standard
were then the
were
analysed
as
experiments,
the
b r o m o p h o s was r e m o v e d b y e x t r a c t i o n
petrolether.
RESULTS Microbial degradation All the microorganisms degraded bromophos to some extent, but the activity varied considerably. Some produced m2PS and mPS, and others produced mainly bPS.
It was not possible to detect mbPSo
Fig. i is a typical chromatogram of microorganisms, Other products, possibly the oxygen analoges of m2PS and mPS were sometimes detected.
A compound
with slightly less R F value than mbPS may be its oxygen analoge (mbPO).
T. li~norum and A. tenius
seem to be particularly active in the bromophos metabolism. Metabolism by the seedlings The seedlings also produced metabolites. was m o s t a c t i v e ,
and the
carrot 108
least
active.
Wheat The
main m e t a b o l i t e s compounds
are
inorganic
w i t h RFO.
phosphates
or other
The o n i o n s e e d l i n g s
produced
m o s t bPS, w h i c h was l o c a t e d Onion seeds
in the
which did not germinate,
metabolites.
In the
bPS a p p e a r e d excellent
mainly
leaves.
p r o d u c e d no
c h r o m a t o g r a m shown
as double spots,
coincidence
there
(fig.
2)
was,
however,
between the carrier
and the
radioactivety.
DISCUSSION The r e s u l t s directly
indicate
by b i o l o g i c a l
phosphorothionates.
that
degradation However,
I f f o r m e d a s an i n t e r m e d i a t e to accumulate transfer are
easily
pounds.
to detectable
reactions,
aPS c a n be f o r m e d of dimethyl
mbPS i s
one s h o u l d amounts.
mbPS a n d o t h e r
reagents~as amines react
(5)
dimethyl
h a s shown t h a t sulfide,
Also in biological
expect
it
By m e t h y l
dimethyl
com-
nucleophilic
thiourea
w i t h m2aPS t o g i v e
stable.
maPS c o m p o u n d s
formed from the analogous Hilgetag
rather
aryl
salts
and tertiary o f maPS.
system~ such methyl transfer
actions
occurs.
Fukami and Shishido
soluble
enzyme s y s t e m which t r a n s f e r r e d
group from methyl parathion
109
(6)
found a a methyl
to glutathione.
re-
C4.,J:,
9169169169
-%
1 F i ~ . 1.
2
3
4
5
6
TLC of p32-bromophos m e t a b o l i t e s formed
by some fungi.
The radioactive metabolites are
dotted and the non-radioactive are encirceled
reference substances
(from top downward: bPS, mbPS, m2PS
and mPS) i, 2, 4, 6: Unidentified soil fungi, 3: Trichoderma !ignorum,
5:
tion time was 9 days.
Alternaria tenius.
Incuba-
Unmetabolised p32-bromophos
was removed by petrolether extraction before chromatography.
110
I 0000o 0@O0o 2
I Fi~.
2.
stances
4
5
The r a d i o a c t i v e
and t h e n o n - r a d i o a c t i v e
reference
are sub-
( f r o m t h e t o p d o w n w a r d s : b r o m o p h o s , bPS,
of germinated wheat. 3: P u r i f i e d
of germinated seeds.
formed
metabolites
mbPS, m2PS a n d mPS) a r e e n c i r c e l e d . wheat.
6
TLC o f p 3 2 - b r o m o p h o s m e t a b o l i t e s
by s e e d l i n g s . dotted
3
2:
The l e a v e s
The s e e d o f g e r m i n a t e d
p32-bromophos.
onion,
1: 4:
The l e a v e s
and 6: u n g e r m i n a t e d
Growing t i m e was 14 d a y s .
111
onion
Hydrolytic degradation by biological systems seems, however, to give the bisdesmethyl compound directly. This may also be the case for other dimethyl aryl phosphorothionates.
REFERENCES 1.
ROWLANDS, D. G.
J.
2.
STIANSI, M. e t a l .
S t o r e d Prod. Res. 2, J. Agric.
1 (1966)
Fd. Chem. 15,
474 (1967) 3.
STENERSEN, J .
4.
ALLEN, O. N.
J.
In p r e s s .
Experiments in Soil Bacteriology
Burgess Publishing 5.
Chromatogr.
HILGETAG, G. e t a l .
Co. M i n n e a p o l i s , J.
prakt.
Minn. 1957.
Chem. 8 ,
207,
(1959). 6.
FUKAMI, J . and SHISHIDO, T. 5_99, 1138 ( 1 9 6 6 ) .
112
J.
econ. Entomol.