degradation of organophosphorus pesticides in aqueous extracts of young green barley leaves (hordeum...
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Degradation of organophosphorus pesticides inaqueous extracts of young green barley leaves(Hordeum vulgare L)Janis J Durham, Joji Ogata, Sadatoshi Nakajima, Yoshihide Hagiwara andTakayuki Shibamoto*Department of Environmental Toxicology, University of California, Davis, CA 95616, USA
Abstract: The degradation of the organophosphorus pesticides malathion, chlorpyrifos, guthion,
diazinon, methidathion and parathion in an aqueous extract of young green barley leaves (Hordeum
vulgare L) was monitored by gas chromatography. Aqueous solutions of various amounts of freeze-
dried young barley leaves containing 5.75mglÿ1 of malathion were incubated at 37°C and pH 7.4 over
prolonged time periods. Over 95% of the malathion degraded in 4h in a 3% (30g lÿ1) solution of young
green barley leaves. When the barley solution was autoclaved at 120°C for 25min prior to the addition
of malathion, no degradation of malathion was observed. When 10mglÿ1 each of the above six
pesticides was incubated in a 15% (150g lÿ1) solution of young green barley leaves for 3h at 37°C and pH
7.4, malathion and chlorpyrifos degraded 100%, whereas parathion (75%), diazinon (54%), guthion
(41%) and methidathion (23%) showed lesser degrees of degradation.
# 1999 Society of Chemical Industry
Keywords: barley leaves; malathion; organophosphorus pesticides; pesticide degradation
INTRODUCTIONAlthough pesticides have made a very important
contribution towards increasing both the quality and
quantity of crop production in the world over the last
half century, concern about the impact of pesticide
residues in foods on human health has grown,
especially in developing countries.1
In order to prevent any possible adverse effects
caused by pesticide residues in foods, such residues
should be reduced as much as possible. However, it is
impossible to completely remove all pesticide residues
from foods. Therefore it is ideal if pesticide residues
can be degraded into non-toxic materials in foods.
Monitoring pesticide degradation in a natural plant
extract is one avenue to investigate the possible
reduction of pesticide residue levels in foods. There
are some reports on the role of food plants in pesticide
degradation. For example, some food plants have been
shown to be capable of metabolically degrading
pesticides;2 also, carrot cell suspension cultures
degraded a pesticide.3
In the present study the degradation of organophos-
phorus pesticides in an aqueous extract of young green
barley leaves was investigated. Aqueous extracts from
young barley leaves were selected for this study
because they are known to contain many enzymes
which may degrade pesticides.4 For example, more
than 20 enzymesÐincluding cytochrome oxidase,
peroxidase, catalase, fatty acid oxidase and trans-
hydrogenaseÐin an aqueous green barley extract were
reported at the Japanese Society of Pharmaceutical
Science.5 Organophosphorus pesticides were chosen
because they are among the most commonly used
insecticides.6 Of the organophosphorus pesticides,
malathion has been the most widely used on various
crops. For example, in 1992, 360tons of malathion
was applied to over 70 crops in California alone.7
MATERIALS AND METHODSReagentsAll reagents were analytical grade (Fisher Scienti®c,
Santa Clara, CA, USA). Malathion, guthion, chlor-
pyrifos, diazinon, methidathion and parathion stan-
dards were purchased from Chem Service Co (West
Chester, PA, USA). Structures of pesticides used in
the present study are shown in Fig 1 along with their
CAS name. A gas chromatographic internal standard
(IS) was prepared by the addition of 60mg of
parathion to 50ml of ethyl acetate. Trizma1 buffer
(pH 7.4) was prepared by combining 13.2g Trizma1
HCl with 1.94g Trizma1 base (both purchased from
Sigma Chemical Co, St Louis, MO, USA) in a 2l
volumetric ¯ask and adding deionised water to
volume. C18 solid phase extraction (SPE) cartridges
were bought from Varian Corp (Harbor City, CA,
USA). Bovine serum albumin (BSA) was purchased
from Bio-Rad Laboratories (Hercules, CA, USA).
Journal of the Science of Food and Agriculture J Sci Food Agric 79:1311±1314 (1999)
* Correspondence to: Takayuki Shibamoto, Department of Environmental Toxicology, University of California, Davis, CA 95616, USA(Received 18 August 1998; revised version received 12 January 1999; accepted 29 March 1999)
# 1999 Society of Chemical Industry. J Sci Food Agric 0022±5142/99/$17.50 1311
Preparation of freeze-dried young green barleyleavesYoung green barley leaves (Hordium vulgare L, var
nudum Hook) were harvested 2 weeks after germina-
tion.8 The young green barley leaves were freeze-dried
for 3 days in a freeze-dryer, Model 50-SRC-5 (VIRTIS
Co, Gardner, NY, USA). The freeze-dried leaves were
subsequently ground with a Wiley Mill Standard
Model No 3 (Arthur H Thomas Co, Philadelphia,
PA, USA) equipped with a 2mm mesh size sieve to
form a ®ne and uniform powder.
Sample preparations for pesticide degradationexperimentsTrizma1 buffer solutions (400g, pH 7.4) containing
powdered barley leaves (4 and 12g) were prepared at
25°C. The resulting mixtures, 1% and 3% concentra-
tions (w/w) of barley samples in the buffer, were stirred
for 10min using a magnetic stirrer. After two table-
spoonfuls of talc or celite were added, the sample
solutions were stirred for an additional 5min. The
sample solutions were subsequently ®ltered and each
®ltrate was divided into three 100ml aliquots to
conduct three replications. A buffer solution (100ml)
without barley was treated as the control preparation.
One of the 3% barley buffer solutions was autoclaved
for 25min at 120°C to deactivate the enzymes.
Each sample was spiked with a 0.5ml acetone
solution of malathion (4.6mgmlÿ1) in a 200ml ¯ask.
After spiking, the ¯asks were sealed and mixed by
inverting each ¯ask several times by hand. These
sample ¯asks were then covered with aluminium foil to
prevent possible photodegradation of the malathion.
The samples were allowed to stand at 25 or 37°C for
the duration of the experiment. Conditions used to
prepare each malathion sample are summarised in
Table 1.
At 10, 30, 60, 120 and 240min after spiking with
malathion, 10ml subsamples were transferred from
each sample into preconditioned C18 SPE cartridges.
Each cartridge was preconditioned with two column
volumes of ethyl acetate, followed by drying atÿ10psi
for 3.5min and then the addition of two column
volumes each of methanol and distilled water. After
Figure 1. Organophosphorus pesticides used in the experiment.
Table 1. Conditions for sample preparations
Sample Barley conc. Solvent Temperature
I 1% Trizma 25°CControl a 0 Trizma 25°C
II 3% Trizma 25°CControl a 0 Trizma 25°C
III 1% Trizma 37°CControl b 0 Trizma 37°C
IV 3% Trizma 37°CControl b 0 Trizma 37°C
V 1% water 37°CControl c 0 water 37°C
VI 3% water 37°CControl c 0 water 37°C
VIIa 3% water 25°CControl d 0 water 25°Ca Barley solutiion was autoclaved at 120°C for 25 min.
1312 J Sci Food Agric 79:1311±1314 (1999)
JJ Durham et al
eluting each subsample, the cartridges were rinsed
with a small amount of distilled water. Subsequently
the cartridges were dried at ÿ10psi for 5min.
Malathion trapped in the cartridges was eluted with
ethyl acetate using a centrifuge. Each cartridge was
placed in a 15ml centrifuge tube and then 1ml of ethyl
acetate was added. The samples were centrifuged for
1min and the process was repeated with 0.5ml of ethyl
acetate. The eluate organic layer and at least three
ethyl acetate rinses were pipette transferred from each
tube to a corresponding 2ml volumetric ¯ask. Excess
solvent was removed under a nitrogen gas stream. Gas
chromatographic IS (0.2ml) was added to each 2ml
sample prior to analysis.
In another experiment, Trizma1 buffer solutions
(400g, pH 7.4) containing various amounts of barley
leaf powder (0, 2.5, 5, 10, 15, 20%) were prepared at
25°C. Solutions were spiked with 10mglÿ1 of chlor-
pyrifos and incubated at 37°C for 3h. The sample
solutions were treated exactly as in the experiment
with malathion. The amount of chlorpyrifos remaining
in the sample solutions was analysed by GC.
Also, Trizma1 buffer solutions (400g, pH 7.4)
containing 15% of barley leaf powder were prepared at
25°C. A solution was spiked with 10mglÿ1 each of
malathion, guthion, chlorpyrifos, diazinon, methi-
dathion and parathion and incubated at 37°C for
3h. The sample solutions were treated exactly as in the
experiment with malathion. The amounts of pesticides
remaining in the sample solutions were analysed by
GC.
Protein measurement in barley solutionsThe Lowry protein determination method used in this
experiment was a simple colorimetric method that has
been commonly used in many laboratories throughout
the world.9 A stock solution of BSA standard was
prepared by adding 10mg of BSA to 10ml of distilled
water. Standard protein solutions (50, 100, 200, 300
and 500mgmlÿ1) to prepare a calibration curve were
prepared in distilled water using the above stock
solution. After Lowry's reagent was added to each
solution, the absorbance at 660nm was measured
using a Hewlett-Packard 8452A diode array spectro-
photometer.
Instrumental analysis for pesticides in barleysolutionsA Hewlett-Packard (HP) 5890 Series II gas chroma-
tograph equipped with a 30m�0.25mm id DB-5
bonded phase fused silica capillary column (J&W
Scienti®c, Folsom, CA, USA) and a ¯ame photo-
metric detector (phosphorus mode) was used for
quantitative analysis of malathion according to the
GC internal standard method reported previously.10
The oven temperature was programmed from 160 to
220°C at 15°C minÿ1 and held for 12min. The
helium carrier gas ¯ow rate was 1.7ml minÿ1 with a
split ratio of 1:16. The injector and detector tempera-
tures were 220 and 225°C respectively.
RESULTS AND DISCUSSIONProtein contents of the samples were 2.4, 7.2, 11 and
31mgmlÿ1 in 1%, 3%, 5% and 15% barley solutions
respectively. The values were obtained using the
calibration curve prepared with BSA (y =0.012x�0.0116). The results of malathion degradation with
barley leaves are shown in Fig 2. The malathion
concentrations in samples I±VI decreased with time
except in the control samples, which remained fairly
constant. For example, the malathion concentration in
the test samples dropped to 63% in 4h, while the
control concentration remained between 87% and
95% (sample I).
More malathion was degraded in the 3% solutions
than in the 1% solutions. Also, malathion degradation
occurred more rapidly at 37°C than at room tempera-
ture. For sample III, malathion degradation in the 1%
barley leaf powder at 37°C (40%) was similar to that
of sample II in 3% barley leaf powder at 25°C (33%).
Thus the increase in temperature and the increase in
barley concentration had a similar effect on the
degradation of malathion. When both temperature
and barley concentration were increased, the greatest
decrease in malathion was observed. In sample IV the
malathion concentration dropped steadily to 5%,
while that of the control stayed between 90% and
96%.
There was no important difference resulting from
the use of water as opposed to buffer. The only change
in solution pH was noted when the temperature was
increased. The buffer pH, which was 7.4 at 25°C,
dropped to 7.2 in both samplesV and VI and control
solutions as the temperature was increased to 37°C,
and remained at that pH throughout the experiment.
The enzymatic degradation of malathion may be
found in the results of sample VII. The results show
that malathion degradation did not occur in the
autoclaved barley samples. This is likely due to loss
of enzyme activity. In the process of autoclaving the
barley solution, all the proteins were probably de-
natured and lost their activity. These results suggest
that the malathion degradation in barley leaves is an
Figure 2. Amounts of malathion remaining in barley solutions overprolonged time period. Refer to Table 1 for the description of samples.
J Sci Food Agric 79:1311±1314 (1999) 1313
Degradation of organophosphorus pesticides in barley leaves
enzymatic process. This experiment also provides
recovery ef®ciency of malathion from the system used.
Over 97% recovery was obtained from the samples
with deactivated proteins (refer to sample VII in Table
1).
Fig 3 shows the percentage of degradation of
chlorpyrifos (10mglÿ1) incubated at 37°C for 3h in
solutions containing various amounts of barley leaf
powder. Values are mean�standard deviation (n =3).
Signi®cant degradation occurred when the barley leaf
concentration increased over 5% (protein content
11mgmlÿ1), and 100% degradation was achieved in
the 15% barley leaf solution.
Fig 4 shows the degradation of six pesticides
(10mglÿ1 each) incubated at 37°C for 3h in a 15%
barley leaf solution. Values are mean�standard
deviation (n =3). Malathion and chlorpyrifos dis-
appeared completely and the remaining pesticides
showed varying degrees of degradation: parathion
75%, diazinon 54%, guthion 41% and methidathion
23%.
Comprehensive analysis of the degraded pesticide
samples was not performed. However, no additional
peak appeared on the GC-FPD of a test solution after
the degradation of malathion (eg sample IV), suggest-
ing that no volatile organic degradation products
containing sulphur or phosphorus were produced.
On the other hand, some highly polar compounds,
such as dimethyl phosphate which requires derivatisa-
tion before analysis by GC, may be present in the
samples. In order to better understand why an
aqueous extract of young green barley leaves degraded
the pesticides used, efforts will be made to determine
the degradation products to elucidate the pathway of
degradation. As mentioned above, it is impossible to
completely remove pesticide residues from food.
Therefore facilitating the degradation of pesticides
with natural plant materials may be one way to
decrease pesticide residues in foods. Investigation on
the actual application of barley extract is in order.
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Figure 3. Degradation of chlorpyrifols (10ppm) incubated at 37°C for 3 h insolutions containing barley leaf powder.
Figure 4. Degradation of organophosphorus (10ppm each) incubated at37°C for 3 h in a 15% barley leaf solution.
1314 J Sci Food Agric 79:1311±1314 (1999)
JJ Durham et al