Subscriber access provided by Gothenburg University Library
Agricultural and Environmental Chemistry
Different toxic effects of racemate, enantiomers, and metabolite of malathion on HepG2 cells using HPLC-QTOF based metabolomics Jin Yan, Wentao Zhu, Biao Xiang, DeZhen Wang, Shu Sheng Tang, Miaomiao Teng, Sen Yan, and Zhiqiang Zhou J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.8b04536 • Publication Date (Web): 23 Jan 2019 Downloaded from http://pubs.acs.org on January 24, 2019
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 32
Journal of Agricultural and Food Chemistry
84x47mm (300 x 300 DPI)
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
1
Different toxic effects of racemate, enantiomers, and
2
metabolite of malathion on HepG2 cells using HPLC-QTOF-
3
based metabolomics
4
Jin Yana, Wentao Zhua, Biao Xiangb, Dezhen Wanga, Shusheng Tangb, Miaomiao Tenga,
5
Sen Yana, and Zhiqiang Zhoua*
6
a. Beijing Advanced Innovation Center for Food Nutrition and Human Health,
7
Department of Applied Chemistry, China Agricultural University, Beijing 100193,
8
China.
9 10
b. College of Veterinary Medicine, China Agricultural University, Beijing 100193, China.
11
*Correspondence to: Zhiqiang Zhou, Department of Applied Chemistry, China
12
Agricultural University, Beijing 100193, P.R. China. E-mail:
[email protected] 13
Jin Yan and Wentao Zhu contributed equally in this study.
14
Abstract
15
Commercial malathion is a racemic mixture that contains two enantiomers, and
16
malathion has adverse effects on mammals. However, whether these two enantiomers
17
have different effects on animals remains unclear. In this study, we tested the effect of
18
racemate, enantiomers, and metabolite of malathion on the metabolomics profile of
19
HepG2 cells. HepG2 cells showed distinct metabolic profiles when treated with rac-
20
malathion, malaoxon, R-(+)-malathion, and S-(-)-malathion, and these differences were
ACS Paragon Plus Environment
Page 2 of 32
Page 3 of 32
Journal of Agricultural and Food Chemistry
21
attributed to pathways in amino acid metabolism, oxidative stress, and inflammatory
22
response. In addition, malathion treatment caused changes in amino acid levels,
23
antioxidants activity and expression of inflammatory genes in HepG2 cells. S-(-)-
24
malathion exhibited stronger metabolic perturbation than its enantiomer and racemate,
25
consistent with S-(-)malathion’s high level of cytotoxicity. R-(+)-malathion treatment
26
caused significant oxidative stress in HepG2 cells, but induced a weaker disturbance in
27
the amino acid metabolism and a pro-inflammatory response compared to S-(-)-
28
malathion and rac-malathion. Malaoxon caused more significant perturbation on
29
antioxidase and a stronger anti-apoptosis effect than its parent malathion. Our results
30
provide insight into the risk assessment of malathion enantiomers and metabolites. We
31
also demonstrate that a metabolomics approach can identify the discrepancy of the toxic
32
effects and underlying mechanisms for enantiomers and metabolites of chiral pesticides.
33
Keywords: metabolomics, malathion, metabolite, enantiomers
34
Introduction
35
Malathion, [O,O-dimethyl-S-(1,2-dicarcethoxyethyl) phosphorodithioate], is an
36
organophosphate that is used as a pesticide to control insect pests on crops, and as an
37
anti-parasitic drug in both animals and humans to eliminate ectoparasites1, 2. Like other
38
organophosphate pesticides, malathion inhibits the enzyme cholinesterase to eliminate
39
insect pests. Malathion is commonly used and there are several modes with which
40
animals and humans may be exposed to malathion, including application in farms and
41
gardens, consumption of contaminated food and water, and entering malathion treated
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
42
areas3. While it is considered to have low toxicity on mammals, it still exhibits adverse
43
effects on the plasma, muscle, and brain of mammals by inhibiting cholinesterase4, and
44
can cause dysfunction of other organ systems, such as liver, kidney5, and testis6.
45
Malathion has a chiral α-carbon atom on the succinyl ligand and has two enantiomers.
46
Both enantiomers display the same physical and chemical properties in non-chiral
47
environments7; however, they have different degradation rates in biological systems.
48
For example, S-malathion degrades faster than R-malathion in soil, water, and several
49
crops8, 9. R-malathion is more persistent in the environment and has stronger
50
insecticidal activity than S-malathion. Malaoxon is the main metabolite of malathion
51
and it is more toxic than malathion in insects. Malaoxon causes DNA damage by
52
inducting oxidization and methylation DNA10, 11, and this may be the underlying reason
53
why commercial malathion acts as a potential mutagen12. However, in the human
54
choriocarcinoma (JAR) cell line, malathion causes cyto- and genotoxic effects before
55
it is metabolized into malaoxon13. Despite this, very limited work has been done to
56
investigate the potential toxic effects of malathion enantiomers and its metabolites on
57
mammals.
58
Metabolomics provides holistic information on endogenous metabolites, and it is a
59
promising tool for toxicology, pharmacology, and oncology. Metabolites are involved
60
in multiple biochemical processes and can reflect the biological status and functioning
61
mechanism of living organs14. Thus, metabolomics can provide insights into the
62
functional mechanisms of the toxic effects of compounds, and help to find biomarkers
63
to indicate exposure to these chemicals15.
ACS Paragon Plus Environment
Page 4 of 32
Page 5 of 32
Journal of Agricultural and Food Chemistry
64
Here, we sought to identify the consequences of low dose malathion exposure on
65
human liver cells by taking a metabolomics approach. Our results provide insights into
66
the underlying mechanisms of malathion cytotoxicity. We compared the metabolic
67
profiles of liver cells treated with racemate, enantiomers, and metabolite of malathion
68
and further verified findings from the metabolomics analysis to elucidate the different
69
effects of the four malathion compounds on mammalian cells.
70
2. Materials and methods
71
2.1 Chemicals
72
Rac-malathion (98.0% purity) was provided by the China Ministry of Agriculture
73
Institute for Control of Agrochemicals. The enantiomers of malathion were prepared
74
following published protocols9. Malaoxon was purchased from Sigma-Aldrich, 3-(4, 5-
75
dimethylthiazol-2-yl)-2, 5-diphenyltetrazolium bromide (MTT) and fetal bovine serum
76
(FBS) was purchased from Zhejiang Tianhang biotechnology Co., Ltd. 25%Trypsin-
77
0.05%EDTA solution, Penicillin-streptomycin solution, non-essential amino acids
78
solution (NEAA), and minimum essential medium (MEM/EBSS) culture medium were
79
purchased from GE Healthcare Life Science. Reactive oxygen species assay kit,
80
annexin V-FITC/PI double staining apoptosis detection kit, catalase (CAT) assay kit,
81
total superoxide dismutase (T-SOD) assay kit, and reduced glutathione (GSH) assay kit
82
were
83
Dimethylsulfoxide (DMSO), sodium chloride (NaCl), disodium hydrogen phosphate
84
(Na2HPO4), sodium bicarbonate (NaHCO3), and potassium dihydrogen phosphate
85
(KH2PO4) were purchased from Sinopharm Chemical Reagent Co., Ltd.
purchased
from
the
Nanjing
Jiancheng
ACS Paragon Plus Environment
Bioengineering
Institute.
Journal of Agricultural and Food Chemistry
86
2.2 Cell culture and treatment
87
HepG2 cells were purchased from the National Infrastructure of Cell-line Resource
88
(Beijing). Cells were cultured in MEM medium with 10% FBS, 1% NEAA, and 100
89
U/mL Penicillin-streptomycin. Cells were placed in a humidified atmosphere with 5%
90
CO2 and 95% air at 37 ℃. The compounds used in experiments were dissolved in
91
DMSO, and the final concentration of DMSO was 1% (v/v) for each treatment.
92
2.3 Cytotoxicity assay
93
Cytotoxicity was measured by the MTT method as described previously16. HepG2
94
cells (1.5×104 cells/well) were seeded on 96-well plates and cultured for 24 h. Fresh
95
media containing increasing concentration of the treatment compound (100, 200, 300,
96
400, 500, 600, 700, and 1000 μΜ of malathion racemate, enantiomers and malaoxon)
97
were then placed on the cells. Six replicates were conducted per concentration and at
98
least three independent experiments were performed. The vehicle control was standard
99
culture media with 1% DMSO. After culturing cells with treatment media for 48 h, 10
100
μl MTT solution (5 mg/ml in sterile water) was added in each well. Cells were placed
101
in 4 h at 37 ℃, the media were removed by injection syringe, and the formazan crystals
102
were dissolved in DMSO. Samples were agitated for 10 min, and the absorption was
103
measured using a spectrophotometer (Multiskan MK3, Thermo Scientific, Pittsburgh,
104
PA) at 492 nm. The cytotoxicity was expressed by EC50 values (50% effects
105
concentration), which were determined using IBM SPSS 21.
106
2.4 Cell viability
107
HepG2 cells were exposed to 5, 50, and 100 μΜ malathion racemate, R-enantiomer,
ACS Paragon Plus Environment
Page 6 of 32
Page 7 of 32
Journal of Agricultural and Food Chemistry
108
S-enantiomer, and malaoxon for 48 h as described above. Cell viability was measured
109
using a spectrophotometer (Multiskan MK3, Thermo Scientific, Pittsburgh, PA) at 492
110
nm via the MTT method, which was identical to the cytotoxicity assay.
111
2.5 Metabolomics analysis
112
HepG2 cells (6×105 cells/well) were seeded on 6-well plates in 2 ml of culture
113
medium. After incubation for 24 h, media containing malathion racemate, R-(+)-
114
malathion, S-(-)-malathion and malaoxon at 5, 50, and 100 μΜ were added. Each
115
treatment was conducted in six replicates. Samples were cultured for 48 h, and cells
116
were washed with PBS three times and harvested using a cell scraper in 1ml PBS. After
117
counting the number of cells using an automated cell counter (Counter Star, Shanghai,
118
China), we transferred the cell pellet into tubes and added 1 ml cold extraction solvent
119
methanol:choloroform (9:1) to quench cellular metabolism. The counted number of
120
cells was used to normalize metabolomics data. Cells were ultrasonicated in an ice bath
121
ultra-sonicator (Sonics Vibra-Cell™, Sonics&Materials Inc, USA) for 5 min, and
122
subsequently centrifuged at 4 ℃ for 5 min at 12,000 g. The supernatant was transferred
123
and divided into two parts, one of which was used for untargeted metabolomics analysis,
124
while the other was used for targeted amino acid analysis.
125
2.5.1 Untargeted metabolomics analysis
126
700 μL supernatant of the cell extractions were collected and dried with a stream of
127
nitrogen. The residues were reconstituted in 500 μL solvent consisting of 60%
128
acetonitrile and 40% water and purified with 0.22 μm filters before HPLC-QTOF
129
analysis. Cell metabolic profiles were obtained using Agilent 1200 series HPLC system
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
130
coupled with Agilent 6510 QTOF mass spectrometry (Agilent, USA). The analysis was
131
performed in reversed-phase column (ACQUITY BEH C18, 150 mm × 2.1 mm, 1.7 μm,
132
Waters, Milford, CT, USA) equipped with a guard cartridge system and maintained at
133
40 ℃. The flow rate was 0.3 mL/min and the mobile phase contained solvents A (10%
134
acetonitrile/90% H2O containing 5 mM ammonium acetate and 0.2% acetic acid) and
135
B (90% acetonitrile/10% H2O containing 5 mM ammonium acetate and 0.2% acetic
136
acid). Samples were passed through a gradient of 10% A for 1.5 min, solvent with
137
linearly increasing concentration of A from 10% to 50% for 3.5 min and held for 7 min;
138
then, samples were returned to 10% A solution for 2 min, and held in 10% A for 16
139
min. Electrospray ionization (ESI) conditions were conducted in the positive and
140
negative electrospray modes in separate runs with full scan mode ranges from m/z 60
141
to 1000. The capillary voltages were 3800 and 4000 V with a scan rate of 1.03 scans
142
per second. The nebulizer gas flow rate was 10 L/min; the pressure was maintained at
143
45 psi and temperature was maintained at 325 ℃. Reference masses 121.0509,
144
922.0098 (positive mode) and 119.0363, 966.0007 (negative mode) were used for
145
continuous and online mass calibration throughout the analyses. Samples were injected
146
in randomized sequence.
147
The Molecular Feature Extractor (MFE) tool in the MassHunter Qualitative Analysis
148
Software (Agilent, USA) was used to clean unrelated ions and background noise from
149
the data files. MFE is an untargeted feature-finding algorithm that can extract individual
150
compound features from QTOF-MS chromatograms even when these are complicated
151
and when compounds are not well resolved. The MFE outputs a list of all possible
ACS Paragon Plus Environment
Page 8 of 32
Page 9 of 32
Journal of Agricultural and Food Chemistry
152
compound features extracted from full scan QTOF data. Then, the MassHunter Mass
153
Profiler Professional Software B.02.00 (Agilent, USA) was used to align and filter
154
extracted features. Absolute abundance above 5000 counts and with a minimum of two
155
ions were chosen for the analysis. Metabolites from different samples were aligned
156
using a retention time window of 0.1% (0.15 min); multiple charge states were not
157
selected. Common features present in > 80% of all samples were analyzed and corrected
158
for individual bias.
159
2.5.2 Analysis of the targeted amino acid metabolism
160
180 μL supernatant of cell extraction was mixed with stable-isotope labeled internal
161
standards (20 μL); then, the samples were derivatized with both reagent I (1-propyl
162
alcohol/3-picoline = 77/23, 80 μL) and reagent II (chloroform/iso-octane/propyl
163
carbonochloridate =71.6/11/17.4, 50 μL). The amino acid derivatives were extracted
164
with ethyl acetate (250 mL), and the supernatant was dried by a stream of nitrogen and
165
then re-dissolved in 200 μL 0.1% formic acid in water.
166
The amino acid concentration was measured using an UltiMate 3000 system plus
167
TSQ Quantum Access Max mass spectrometer (Thermo Fisher Scientific). An EZ:faast
168
4u AAA-MS column (250 mm x 2.0 mm, 4 μm, Phenomenex, USA) was used to
169
separate the amino acids using both mobile phase A (acetonitrile with 0.1v% formic
170
acid) and mobile phase B (water with 0.1 v% formic acid) at an injection volume of 5.0
171
uL and a flow rate of 0.3 mL/min. The mobile phase constituent began with 62% A and
172
38% B, was then linearly increased to 79% A and 21% B for 12 min, and adjusted back
173
to 62% A and 38% B for 4 min. Experimental results were processed using Xcalibur
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
174
2.2 (Thermo Fisher Scientific).
175
2.6 Antioxidant assays
Page 10 of 32
176
HepG2 cells were seeded in 6-well plates with 7×105 cells/well density and exposed
177
to the four compounds for 48 h. Subsequently, the media was removed by vacuum
178
pump and cells were rinsed with phosphate buffered saline (PBS) three times. Cells
179
solution were obtained by cell scraper with PBS, and the cell pellets were collected
180
after centrifugation at 1000 × g for 5 min and stored in -80 ℃. Cells were suspended in
181
1 ml PBS, sonicated for 2 min using an ice bath ultra-sonicator (Sonics Vibra-Cell™,
182
Sonics&Materials Inc, USA), and centrifuged at 4000 × g for 5 min. Supernatants were
183
obtained to measure the antioxidant GSH and antioxidant enzymes catalase (CAT),
184
superoxide dismutase (SOD) using UV-2600 spectrophotometer (Shimadzu, Japan)
185
according to the instructions of the test kits from the Nanjing Jiancheng Bioengineering
186
Institute (Nanjing, China). All results represent three independent experiments.
187
2.6. Gene expression analysis
188
HepG2 cells were seeded in 6-well plates with 6×105 cells/well density and
189
exposed to the four compounds for 48 h. The expression level of genes involved in the
190
inflammatory response, cyclooxygenase-2 (COX-2) and nuclear factor-kappa B (NF-
191
κB),
192
lymphoma/leukemia-2gene (Bcl-2), and Bcl-2-associated X protein (Bax), were
193
measured using qRT-PCR. Primer sequences are listed in Table S1. Total RNA was
194
extracted from cells using RNA isolation kit (Tiangen, Beijing, China) following the
195
manufacturer’s protocol. NanoDrop 2000c spectrophotometer (Thermo Scientific,
and
genes
involved
in
apoptosis,
caspase-3,
ACS Paragon Plus Environment
caspase-9,
B-cell
Page 11 of 32
Journal of Agricultural and Food Chemistry
196
Wilmington, DE) was used to measure the concentration of the total extracted RNA.
197
The quality of the total RNA was assessed by the ratio of absorbance (A260/A280) and
198
the integrity of banding pattern on a 2% agarose gel. 1 μg of total RNA was reverse
199
transcribed to cDNA using the FastQuant RT Kit (with gDNAase) (Tiangen, Beijing,
200
China). Quantitative real-time PCR was performed with 1 μL of the cDNA template
201
with the SuperReal premix Plus (SYBR Green) Kit on an ABI-7500 system (Advanced
202
Biosystems, Foster, California, USA). Experiments were performed at least three times.
203
2.7 Western blotting analysis
204
HepG2 cells were seeded on to 6-well culture plates at a density of 6×105 cells/well
205
and treated with 100 μM four malathion compounds at 37 °C for 48 h. Cells were
206
harvested and lysed in 100 μL ice-cold lysis buffer. The supernatants of lysates were
207
collected following ultrasonication and centrifugation. The protein concentrations were
208
measured with Pierce BCA Protein Assay Kit (Thermo Fisher Scientific). Western
209
blotting was conducted with 150 μg protein per lane. The primary antibodies of rabbit
210
polyclonal antibodies against caspase 3 and COX-2 were employed. The following
211
secondary antibodies were employed: goat anti-rabbit IgG or rabbit anti-mouse IgG
212
(Zhongshan Golden Bridge Co., Beijing, China). The results were normalized to either
213
the β-actin standard and analyzed using ImageJ (National Institute of Mental Health,
214
Bethesda, MD, USA).
215
2.7 Statistical analysis
216
SIMCA P+ (Version 13, Umetrics, Sweden) was used for multivariate statistical
217
analysis of metabolomics data. Principal component analysis (PCA) was performed to
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 12 of 32
218
investigate the intrinsic clusters of different groups and to search for possible outliers.
219
Partial least-squares discriminant analysis (PLS-DA) was subsequently conducted on
220
the Q-TOF datasets to uncover treatment-related differences. Metabolite differences in
221
cells after exposure to DMSO, malathion racemate, enantiomers, and malaoxon were
222
evaluated using student’s t-test. Variable importance in the project (VIP) > 1 and p
1 and student’s t test p < 0.05,
275
and found 78, 42, 85, and 50 altered endogenous metabolites in HepG2 cells treated
276
with rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon, respectively.
277
Metabolites that were affected by malathion compounds included carbohydrates, amino
278
acids, nucleosides, fatty acids, phospholipids, and carboxylic acids (Table S2).
279
Metabolic profiles were most perturbed under S-(-)-malathion treatment, followed by
280
rac-malathion, malaoxon, and R-(+)-malathion. These results were similar to the
281
cytotoxicity assays, where S-(-)-malathion resulted in the most severe effects. A total
282
of 26 metabolites were changed in cells exposed to malathion racemate and its two
283
enantiomers (Fig. 3A). More metabolites were affected only by one of the three
ACS Paragon Plus Environment
Page 14 of 32
Page 15 of 32
Journal of Agricultural and Food Chemistry
284
compounds. Moreover, rac-malathion and S-(-)-malathion caused similar changes in
285
26 metabolites, while only one metabolite was shared in the metabolic changes induced
286
by rac-malathion and R-(+)-malathion. These results indicate that metabolic profiling
287
changes induced by R-(+)-malathion and S-(-)-malathion were enantio-selective, and
288
the metabolome of S-(-)-malathion treatment was similar to that of rac-malathion
289
treatment. Metabolic changes in the rac-malathion and malaoxon treatment conditions
290
shared 35 metabolites; however, both compounds still induced changes that were
291
unique to each compound in HepG2 cells (Fig. 3B).
292
We next identified the metabolic pathways that were altered by the four compounds.
293
HepG2 cells exposed to rac-malathion (Fig.4), showed significant changes in
294
glycerophospholipid metabolism, arginine and proline metabolism, alanine, aspartate
295
and glutamate metabolism, arachidonic acid metabolism, pantothenate and CoA
296
biosynthesis, phenylalanine metabolism, lysine degradation, aminoacyl-tRNA
297
biosynthesis, glutamine and glutamate metabolism, as well as lysine biosynthesis. S-(-)-
298
malathion affected seven metabolic pathways, all of which were also affected by rac-
299
malathion. Six metabolic pathways were affected by R-(+)-malathion treatment, and
300
the most significant change occurred in taurine and hypotaurine metabolism. This is a
301
pathway that was not affected by exposure to rac-malathion and S-(-)-malathion. R-(+)-
302
malathion exposure also affected glycine, serine, and threonine metabolism, a pathway
303
that was significant only in this treatment. Only four metabolic pathways were
304
significantly affected by malaoxon exposure, including the histidine metabolism, which
305
was unique to this treatment. These results suggest that changes of the metabolic
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
306
pathways caused by R-(+)-malathion and S-(-)-malathion were also enantio-selective.
307
Changes in metabolic pathways that were induced by S-(-)-malathion exposure were
308
similar to rac-malathion exposure. Moreover, malathion treatment resulted in the
309
disruption of more pathways than malaoxon treatment. In addition, the metabolic
310
pathways that were disrupted by exposure to the four malathion compounds were highly
311
related to the amino acid metabolism, taurine and hypotaurine metabolism,
312
glycerophospholipid metabolism, and arachidonic acid metabolism.
313
3.3 Amino acid metabolism
314
To further investigate the effects of malathions on amino acid metabolism, we
315
quantified amino acid levels using a targeted HPLC-MS/MS approach with stable
316
isotope-labeled internal standard. We found that levels of serine, asparaginate, glycine,
317
alanine, lysine, proline, glutamate, phenylalanine, valine, leucine, and glutamine were
318
significantly affected by the four malathion compounds (Fig. 5). Moreover, rac-
319
malathion exposure, which induced changes in eight metabolites, led to the strongest
320
perturbation of amino acid levels, followed by S-(-)-malathion and malaoxon. Only
321
levels of two amino acids were altered by R-(+)-malathion exposure; therefore, R-(+)-
322
malathion showed the weakest effect on amino acids in HepG2 cells.
323
3.4 Antioxidant activity
324
The four tested compounds altered several endogenous metabolites that are related
325
to oxidative stress in cells. We tested for changes of oxidative stress by measuring
326
antioxidant activity and differences in redox homeostasis in cells treated with the four
327
compounds. SOD converts O2- to H2O2, and its activity levels were reduced in the R-
ACS Paragon Plus Environment
Page 16 of 32
Page 17 of 32
Journal of Agricultural and Food Chemistry
328
(+)-malathion treatment for all dosages. SOD activity was not affected by rac-
329
malathion treatment, and only 5 μM malaoxon treatment decreased SOD activity. All
330
three doses of S-(-)-malathion altered SOD activity, and SOD activity levels were
331
decreased in low and medium dose treatments, but increased in the high dose treatment.
332
The activity of CAT, a scavenger of H2O2, was reduced after exposure to 5 μM R-(+)-
333
malathion, as well as 50 μM R-(+)-malathion and malaoxon. GSH content, which also
334
converts O2- to H2O2, were decreased after exposure to 5 μM of rac-malathion, R-(+)-
335
enantiomer, S-(-)-enantiomer, and malaoxon. Surprisingly, the GSH content was not
336
affected in HepG2 cells treated with high doses of the four malathion compounds.
337
These results suggest that R-(+)-malathion caused stronger oxidative stress compared
338
to the other compounds, and the metabolite malaoxon perturbed antioxidants more than
339
its parent malathion.
340
3.5 mRNA expression of inflammatory genes
341
Arachidonic acid metabolism disorder contributes to inflammatory response;
342
therefore, we investigated the expression of cyclooxygenases-2 (COX-2), which is an
343
immediate-early response gene for inflammation. Rac-malathion, R-(+)-malathion, S-
344
(-)-malathion, and malaoxon treatment induced a significant and dose-dependent up-
345
regulation of COX-2 gene in HepG2 cells (Fig. 7). In addition, expression levels of the
346
inflammatory transcription factor NF-κB were also higher in cells treated with the four
347
malathion compounds. These obtained results suggest that exposure to malathion
348
compounds led to pro-inflammatory activity in HepG2 cells. Furthermore, R-(+)-
349
malathion did not alter gene expression levels of COX-2 and NF-kB in low dose
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
350
treatment, and presented the lowest effect on inflammatory response.
351
3.6 mRNA expression of apoptosis genes
352
Exposure to cytotoxic compounds can induce apoptosis; therefore, we tested
353
whether treatment with malathion compounds altered gene expression of caspase-3,
354
caspase-9, bax, and bcl-2 (Fig. 8). Expressions of the pro-apoptotic genes caspase-3
355
caspase-9, and bax were not affected by exposure to the four malathion compounds.
356
However, the expression level of bcl-2, an anti-apoptotic gene that delays the
357
progression of mitochondrial pathways in apoptosis, was up-regulated in a dose
358
dependent manner upon treatment with the four malathion compounds. These results
359
suggested that malathion compounds had an anti-apoptosis effect on HepG2 cells, and
360
no significant differences in anti-apoptosis ability were observed among the four tested
361
compounds.
362
3.7 Protein content of caspase 3 and COX-2
363
To confirm the effect of the four malathion compounds on inflammatory and
364
apoptosis response, HepG2 cells were exposed to 100 μM rac-malathion, R-(+)-
365
malathion, S-(-)-malathion, and malaoxon. The results of Western blot revealed that all
366
the malathion compounds elicited an increase in COX-2 (Fig. 9). Rac-malathion
367
induced the strongest expression of COX-2 compared to others. Similar to gene
368
expression, the induction of COX-2 protein in R-(+)-malathion exposure group which
369
presented the lowest effect on inflammatory response in gene expression was modest.
370
Moreover, the caspase 3 protein was not changed in cells exposed to rac-malathion, R-
371
(+)-malathion, S-(-)-malathion, and malaoxon.
ACS Paragon Plus Environment
Page 18 of 32
Page 19 of 32
372
Journal of Agricultural and Food Chemistry
4. Discussion
373
Most molecules within living organism are chiral compounds. Malathion is one of
374
the most commonly used chiral organophosphate pesticide, and has two enantiomers:
375
R-(+)-malathion and S-(-)-malathion. Thus, the enantiomers of malathion may interact
376
differently in living systems, making it stereo-selection, and several studies have
377
reported the stereo-selective acute toxicity of malathion enantiomers in living organism.
378
However, how different enantiomers of malathion cause toxicity in mammals are
379
unclear. In present study, we took a metabolomics approach to test how low doses of
380
rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon affect the metabolome
381
of HepG2 cells and clarify the underlying toxic mechanism of malathion compounds.
382
Exposure to rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon all
383
affected the survival of HepG2 cells. S-(-)-malathion showed highest cytotoxicity in
384
HepG2 cells in comparison to the other malathion compounds. However, these results
385
were inconsistent with previous studies that report R-(+)-malathion as having the
386
strongest toxic effect on Daphnia magna, earthworms and honeybees, followed by rac-
387
malathion, and S-(-)-malathion9,
388
difference in the micro-environment between tissues in vivo and in vitro. Similar toxic
389
differences were also observed in isomers of endosulfan, where β-endosulfan had
390
higher toxicity on HepG2 and SH-SY5Y cells than α-endosulfan19, 20; however, toxicity
391
of α-endosulfan was higher than that of β-endosulfan in Daphnia, rainbow trout, and
392
Hyalella in vivo21.
393
17, 18.
This inconsistency may be caused by the
The metabolomics profiles of HepG2 cells were significantly changed by exposure
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
394
to rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon at concentrations
395
that did not result in cell death. PCA and PLS-DA revealed that metabolic perturbations
396
were different and enantio-selective, and the patterns were similar to the results of the
397
cytotoxicity test. S-(-)-malathion treatment resulted in the strongest disturbance on the
398
cell metabolome, with 85 metabolites altered, followed by rac-malathion, malaoxon,
399
and R-(+)-malathion. Changes in metabolites were related to several metabolic
400
pathways, and these may shed light on the underlying mechanism for different toxicity
401
of malathion racemate, enantiomers, and metabolite.
402
Amino acid and their metabolites are important for building proteins and
403
polypeptides as well as regulating cell growth, reproduction, and immunity. Disordered
404
amino acid levels could cause neurological disorders, oxidative stress, cardiovascular
405
disease, and cell death22. According to the results of metabolic pathways analysis, many
406
pathways altered by the four malathion compounds were involved in the amino acid
407
metabolism. We quantified amino acid concentrations and found that rac-malathion,
408
malaoxon, R-(+)-malathion, and S-(-)-malathion caused significant changes in amino
409
acid levels, but to different extent.
410
Serine is a nonessential amino acid and plays an important role in cell proliferation.
411
It showed increase in levels after exposure to rac-malathion, malaoxon, and S-(-)-
412
malathion. In cells, serine can be derived from glycine, which is regarded as an indicator
413
of cancer cell proliferation23. Treatment of malaoxon and S-(-)-malathion induced a
414
significant increase in the glycine level. These results suggest that malathion
415
compounds may induce proliferation of HepG2 cells and these changes are stereo-
ACS Paragon Plus Environment
Page 20 of 32
Page 21 of 32
Journal of Agricultural and Food Chemistry
416
selective. HepG2 cells exposed to low levels of malathion showed increase in cell
417
proliferation24, and inductions of proliferation by malathion were also observed in rat
418
mammary gland25 and earthworms spermatogonia26. Changes in asparagine and
419
glutamine may be related to toxic effects of malathion on the immune function27, and
420
changes induced by rac-malathion differed to other malathion compounds. Moreover,
421
the amounts of glutamate, phenylalanine, leucine, proline, and lysine were also
422
decreased to different extent in HepG2 cells that were exposed to one or two malathion
423
compounds. The decreased amino acid levels observed in malathion treated cells may
424
account for the increase of protein synthesis, which was also observed in fish exposed
425
to malathion28-30. More importantly, this is the first investigation of the different effects
426
of racemate, enantiomers, and metabolite of malathion on amino acid metabolism, and
427
R-(+)-malathion, which only induced changes in two amino acids, showing the weakest
428
disturbance to amino acid metabolism compared to the other three compounds.
429
Several amino acid changes observed in the experiment above were related to
430
oxidative stress. The taurine and hypotaurine metabolism pathway, which was involved
431
in oxidative stress, was also affected by R-(+)-malathion and malaoxon. We also found
432
that levels of taurine, which have efficacy against chemical-induced oxidative stress31,
433
32,
434
product of glutathione formation and is involved in the antioxidant defense. S-(-)-
435
malathion treatment reduced spermidine levels in HepG2 cells. The metabolite of
436
spermidine (spermine) can prevent glutathione release33 and was increased after
437
exposure to rac-malathion and malaoxon. Changes in these metabolites suggest that the
were increased in HepG2 cells after exposure to malaoxon. Spermidine is a by-
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
438
redox balance in HepG2 cells was disordered. In accordance with this, we observed
439
decreased levels of glutathione in cells exposure to the four malathion compounds.
440
Except for glutathione, cells always express an elaborate array of antioxidant
441
enzymes to eliminate free radicals. SOD and CAT are enzymes that convert superoxide
442
anion (O2-) to hydrogen peroxide (H2O2) and reduce H2O2 to water34. R-(+)-malathion
443
and malaoxon treatment caused significant decreases in CAT and SOD activities;
444
moreover, SOD activity was affected by S-(-)-malathion exposure. Cells tend to
445
regulate their enzymatic system as well as their endogenous metabolites to remove the
446
ROS and maintain the redox homeostasis when exposed to xenobiotic compounds.
447
However, xenobiotics deplete antioxidants and disturb the redox state, thus resulting in
448
oxidative stress and oxidative damage35, 36.
449
Our results suggest that HepG2 cells regulated levels of antioxidative enzymes and
450
metabolites to resist oxidative stress when exposed to the four malathion compounds.
451
Rac-malathion exposure induced significant changes in antioxidants without altering
452
CAT and SOD activity levels. This implies that cells exposed to rac-malathion undergo
453
a different oxidative stress response compared to after exposure to the other three
454
compounds. In addition, changes in oxidative stress resistance induced by malathion
455
were not dose dependent in a predictable way, and the reaction was more sensitive when
456
cells were exposed to low dose of malathion compounds. Previous studies have also
457
shown that malathion induces ROS production and causes oxidative stress in diverse
458
organs24, 37-41, and exposure to low dose of malathion alters CAT and SOD activities in
459
liver, kidney, lung, diaphragm, quadriceps, and brain39, 42. Here, we firstly compared
ACS Paragon Plus Environment
Page 22 of 32
Page 23 of 32
460
Journal of Agricultural and Food Chemistry
the different effects of racemate, enantiomers, and metabolite of malathion.
461
Oxidative stress induces inflammation response and apoptosis43. In our study, we
462
found evidence that malathion treatment induces an inflammation response in HepG2
463
cells. This non-targeted metabolomics study showed that glycerophospholipid
464
metabolism (i.e. LysoPC and PC) was altered after exposure to the four malathion
465
compounds. LysoPC is involved in inflammatory diseases and regulates formation of
466
arachidonic acid44, and LysoPC(18:1) stimulates IL-1β production in human
467
monocytes45. LysoPC(18:1(9Z)) levels were altered in HepG2 cells exposed to S-(-)-
468
malathion and rac-malathion, and perturbation of arachidonic acid metabolic pathway
469
was observed in rac-malathion, S-(-)-malathion, and malaoxon treatments. We also
470
observed a significant increase in arachidonic acid in cells exposed to the four
471
compounds. Arachidonic acid mediates inflammation and organ function either directly
472
or upon conversion to eicosanoids. PGE2 is an eicosanoid synthesized from arachidonic
473
acid through cyclooxygenase-2 (COX-2), and it activates the secretion of IL-1α and IL-
474
246. We found elevated gene and protein expression of COX-2 after exposure to the
475
four malathion compounds. In summary, these results suggest that malathion compound
476
treatment triggers an inflammatory response in cells.
477
NF-κB is a transcription factor that regulates stress response47, and its activation
478
regulates the expression of COX-2 to promote inflammation48. Exposure to the four
479
malathion compounds caused a significant increase in NF-κB mRNA expression,
480
suggesting that changes in COX-2 expression may be mediated by the NF-κB signal
481
transduction pathway. These findings are consistent with previous studies that showed
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 24 of 32
482
that malathion induced inflammatory responses and stimulated hepatic cytokines to
483
active NF-κB in the rat liver49. In addition, both arachidonic acid and LysoPC(18:1(9Z))
484
levels were not affected by R-(+)-malathion treatment, and changes in gene expression
485
of COX-2 and NF-kB were not as striking in low dose of R-(+)-malathion treatment
486
compared to the other compounds; therefore, R-(+)-malathion may result in a weaker
487
inflammatory response.
488
Apoptosis, known as a form of programmed cell death, can be triggered by
489
exogenous chemicals and mitochondria-generated ROS50,
51.
490
(DPA) reduces tumor growth by inhibiting bcl-252, 53 and its levels were increased in
491
cells exposed to the four malathion compounds. However, we observed enhanced
492
expression of bcl-2 while the expression of bax remained unchanged, which may tilt
493
the cells toward survival and render tumor cells more resistant to chemical-induced
494
apoptosis54. The increase in bcl-2 expression may be a result of the increased NF-κB
495
expression induced by these compounds, which can counteract cell death through
496
delivering anti-apoptotic signals55. The increase in DPA levels may be a stress response
497
in cells to resist toxic effects induced by these compounds. Further studies on
498
malathion-induced apoptosis will clarify the underlying mechanisms in the future.
Docosapentanoic acid
499
We used a metabolomics approach to identify the metabolic perturbations in HepG2
500
cells induced by rac-malathion, malaoxon, R-(+)-malathion, and S-(-)-malathion. We
501
aimed to explore the mechanisms underlying cytotoxicity in mammalian cells by the
502
chiral pesticides. The obtained results of the present study revealed that exposure to the
503
four malathion compounds caused significant changes in metabolic profiles of HepG2
ACS Paragon Plus Environment
Page 25 of 32
Journal of Agricultural and Food Chemistry
504
cells compared to control. Changes in metabolic profiles were involved in multiple
505
aetiologies and pathogeneses, including amino acid metabolism, oxidative stress, and
506
inflammatory response. Moreover, we verified results of the metabolomics analysis and
507
found that amino acid levels, antioxidant activity, and expression of inflammatory
508
genes were also changed after exposure to the four compounds. In addition, rac-
509
malathion, malaoxon, R-(+)-malathion, and S-(-)-malathion treatment resulted in a
510
unique profile of changes in HepG2 cells, suggesting that while they share several core
511
similarities, each compound has different effects on cells. For example, malathion
512
treatment resulted in a stronger disturbance of cell metabolic profile than malaoxon. R-
513
(+)-malathion showed weaker effects on amino acid metabolism and pro-inflammatory
514
response than S-(-)-malathion and rac-malathion. Our results illustrate that
515
metabolomics is a powerful tool for assessing the toxic effect of chiral pesticides and
516
can provide data for health risk assessment of malathion at holistic levels.
517
Acknowledgement
518
Funding was provided by the National Key Research and Development Program of
519
China (2016YFD0200202), the National Natural Science Foundation of China
520
(21337005), and the Young Elite Scientists Sponsorship Program by CAST.
521
References
522 523 524 525 526 527 528 529
1.
Elston, D. M., Controversies concerning the treatment of lice and scabies. Journal of the American
Academy of Dermatology 2002, 46, 794-796. 2.
Kalender, S.; Uzun, F. G.; Durak, D.; Demir, F.; Kalender, Y., Malathion-induced hepatotoxicity in
rats: The effects of vitamins C and E. Food and chemical toxicology 2010, 48, 633-638. 3.
Jensen, I. M.; Whatling, P., Malathion: A review of toxicology. In Hayes' Handbook of Pesticide
Toxicology (Third Edition), Elsevier: 2010; pp 1527-1542. 4.
Flessel, P.; Quintana, P. J. E.; Hooper, K., GENETIC TOXICITY OF MALATHION - A REVIEW.
Environmental and Molecular Mutagenesis 1993, 22, 7-17.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
530 531 532 533 534 535 536 537 538 539 540 541 542 543 544 545 546 547 548 549 550 551 552 553 554 555 556 557 558 559 560 561 562 563 564 565 566 567 568 569 570 571 572 573
5.
Al-Othman, A. M.; Al-Numair, K. S.; El-Desoky, G. E.; Yusuf, K.; Al Othman, Z. A.; Aboul-Soud, M. A.
M.; Giesy, J. P., Protection of alpha-tocopherol and selenium against acute effects of malathion on liver and kidney of rats. African Journal of Pharmacy and Pharmacology 2011, 5, 1263-1271. 6.
Uzun, F. G.; Kalender, S.; Durak, D.; Demir, F.; Kalender, Y., Malathion-induced testicular toxicity
in male rats and the protective effect of vitamins C and E. Food and chemical toxicology 2009, 47, 19031908. 7.
Berkman, C. E.; Thompson, C. M., SYNTHESIS OF CHIRAL MALATHION AND ISOMALATHION.
Tetrahedron Letters 1992, 33, 1415-1418. 8.
Sun, M.; Liu, D.; Zhou, G.; Li, J.; Qiu, X.; Zhou, Z.; Wang, P., Enantioselective Degradation and Chiral
Stability of Malathion in Environmental Samples. Journal of Agricultural and Food Chemistry 2012, 60, 372-379. 9.
Sun, M.; Liu, D.; Dang, Z.; Li, R.; Zhou, Z.; Wang, P., Enantioselective behavior of malathion
enantiomers in toxicity to beneficial organisms and their dissipation in vegetables and crops. Journal of hazardous materials 2012, 237, 140-146. 10. Błasiak, J.; Kowalik, J., Protective action of sodium ascorbate against the DNA-damaging effect of malaoxon. Pesticide Biochemistry and Physiology 1999, 65, 110-118. 11. Blasiak, J.; Stańkowska, D., Genotoxicity of Malaoxon: Induction of oxidized and methylated bases and protective effect of α-Tocopherol. Pesticide Biochemistry and Physiology 2001, 71, 88-96. 12. Błasiak, J.; Jałoszynski, P.; Trzeciak, A.; Szyfter, K., In vitro studies on the genotoxicity of the organophosphorus insecticide malathion and its two analogues. Mutation Research/Genetic Toxicology and Environmental Mutagenesis 1999, 445, 275-283. 13. Galántai, R.; Emődy-Kiss, B.; Somosy, Z.; Bognár, G.; Horváth, G.; Forgács, Z.; Gachályi, A.; Szilasi, M., Does malaoxon play a role in the geno-and cytotoxic effects of malathion on human choriocarcinoma cells? Journal of Environmental Science and Health, Part B 2011, 46, 773-779. 14. Corona, G.; Rizzolio, F.; Giordano, A.; Toffoli, G., Pharmaco-metabolomics: An emerging “omics” tool for the personalization of anticancer treatments and identification of new valuable therapeutic targets. Journal of cellular physiology 2012, 227, 2827-2831. 15. García-Cañaveras, J. C.; Castell, J. V.; Donato, M. T.; Lahoz, A., A metabolomics cell-based approach for anticipating and investigating drug-induced liver injury. Scientific reports 2016, 6, 27239. 16. Berridge, M. V.; Tan, A. S., Characterization of the cellular reduction of 3-(4, 5-dimethylthiazol-2yl)-2, 5-diphenyltetrazolium bromide (MTT): subcellular localization, substrate dependence, and involvement of mitochondrial electron transport in MTT reduction. Archives of biochemistry and biophysics 1993, 303, 474-482. 17. Sun, M.; Liu, D.; Zhou, G.; Li, J.; Qiu, X.; Zhou, Z.; Wang, P., Enantioselective degradation and chiral stability of malathion in environmental samples. Journal of agricultural and food chemistry 2011, 60, 372-379. 18. Zhang, A.; Xie, X.; Ye, J.; Lin, C.; Hu, X., Stereoselective toxicity of malathion and its metabolites, malaoxon and isomalathion. Environmental chemistry letters 2011, 9, 369-373. 19. Lu, Y.; Morimoto, K.; Takeshita, T.; Takeuchi, T.; Saito, T., Genotoxic effects of alpha-endosulfan and beta-endosulfan on human HepG2 cells. Environmental Health Perspectives 2000, 108, 559. 20. Enhui, Z.; Na, C.; MengYun, L.; Jia, L.; Dan, L.; Yongsheng, Y.; Ying, Z.; DeFu, H., Isomers and their metabolites of endosulfan induced cytotoxicity and oxidative damage in SH-SY5Y cells. Environmental Toxicology 2016, 31, 496-504. 21. Wan, M. T.; Kuo, J.; Buday, C.; Schroeder, G.; Van Aggelen, G.; Pasternak, J., Toxicity of-,-,(+)-
ACS Paragon Plus Environment
Page 26 of 32
Page 27 of 32
574 575 576 577 578 579 580 581 582 583 584 585 586 587 588 589 590 591 592 593 594 595 596 597 598 599 600 601 602 603 604 605 606 607 608 609 610 611 612 613 614 615 616 617
Journal of Agricultural and Food Chemistry
endosulfan and their formulated and degradation products to Daphnia magna, Hyalella azteca, Oncorhynchus mykiss, Oncorhynchus kisutch, and biological implications in streams. Environmental Toxicology and Chemistry 2005, 24, 1146-1154. 22. Wu, G., Amino acids: metabolism, functions, and nutrition. Amino acids 2009, 37, 1-17. 23. Jain, M.; Nilsson, R.; Sharma, S.; Madhusudhan, N.; Kitami, T.; Souza, A. L.; Kafri, R.; Kirschner, M. W.; Clish, C. B.; Mootha, V. K., Metabolite profiling identifies a key role for glycine in rapid cancer cell proliferation. Science 2012, 336, 1040-1044. 24. Moore, P. D.; Yedjou, C. G.; Tchounwou, P. B., Malathion-induced oxidative stress, cytotoxicity, and genotoxicity in human liver carcinoma (HepG2) cells. Environmental Toxicology 2010, 25, 221-226. 25. Cabello, G.; Valenzuela, M.; Vilaxa, A.; Durán, V.; Rudolph, I.; Hrepic, N.; Calaf, G., A rat mammary tumor model induced by the organophosphorous pesticides parathion and malathion, possibly through acetylcholinesterase inhibition. Environmental Health Perspectives 2001, 109, 471. 26. Espinoza-Navarro, O.; Bustos-Obregón, E., Effect of malathion on the male reproductive organs of earthworms, Eisenia foetida. Asian journal of andrology 2005, 7, 97-101. 27. Galloway, T.; Handy, R., Immunotoxicity of organophosphorous pesticides. Ecotoxicology 2003, 12, 345-363. 28. Uno, S.; Shintoyo, A.; Kokushi, E.; Yamamoto, M.; Nakayama, K.; Koyama, J., Gas chromatography– mass spectrometry for metabolite profiling of Japanese medaka (Oryzias latipes) juveniles exposed to malathion. Environmental Science and Pollution Research 2012, 19, 2595-2605. 29. McCarthy, I. D.; Fuiman, L. A., Growth and protein metabolism in red drum (Sciaenops ocellatus) larvae exposed to environmental levels of atrazine and malathion. Aquatic toxicology 2008, 88, 220229. 30. Sahib, I. K. A.; Rao, K. P.; Rao, K. S.; Rao, K. R., Sublethal toxicity of malathion on the proteases and free amino acid composition in the liver of the teleost, Tilapia mossambica (Peters). Toxicology letters 1984, 20, 59-62. 31. Gürer, H.; Özgünes, H.; Saygin, E.; Ercal, N., Antioxidant effect of taurine against lead-induced oxidative stress. Archives of environmental contamination and toxicology 2001, 41, 397-402. 32. Balkan, J.; Dogğru-Abbasoğlul, S.; Kanbaglil, Ö.; Cevikbas, U.; Aykac-Toker, G.; Uysal, M., Taurine has a protective effect against thioacetamide-induced liver cirrhosis by decreasing oxidative stress. Human & experimental toxicology 2001, 20, 251-254. 33. Rigobello, M.; Toninello, A.; Siliprandi, D.; Bindoli, A., Effect of spermine on mitochondrial glutathione release. Biochemical and biophysical research communications 1993, 194, 1276-1281. 34. R Buettner, G., Superoxide dismutase in redox biology: the roles of superoxide and hydrogen peroxide. Anti-Cancer Agents in Medicinal Chemistry (Formerly Current Medicinal Chemistry-AntiCancer Agents) 2011, 11, 341-346. 35. Bayir, H., Reactive oxygen species. Critical Care Medicine 2005, 33, S498-S501. 36. Apel, K.; Hirt, H., Reactive oxygen species: Metabolism, oxidative stress, and signal transduction. Annual Review of Plant Biology 2004, 55, 373-399. 37. Akhgari, M.; Abdollahi, M.; Kebryaeezadeh, A.; Hosseini, R.; Sabzevari, O., Biochemical evidence for free radical-induced lipid peroxidation as a mechanism for subchronic toxicity of malathion in blood and liver of rats. Human & experimental toxicology 2003, 22, 205-211. 38. Delgado, E. H. B.; Streck, E. L.; Quevedo, J. L.; Dal-Pizzol, F., Mitochondrial respiratory dysfunction and oxidative stress after chronic malathion exposure. Neurochemical Research 2006, 31, 1021-1025. 39. Fortunato, J. J.; Feier, G.; Vitali, A. M.; Petronilho, F. C.; Dal-Pizzol, F.; Quevedo, J., Malathion-
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
618 619 620 621 622 623 624 625 626 627 628 629 630 631 632 633 634 635 636 637 638 639 640 641 642 643 644 645 646 647 648 649 650 651 652 653 654 655 656 657 658 659
induced oxidative stress in rat brain regions. Neurochemical research 2006, 31, 671-678. 40. Durak, D.; Uzun, F. G.; Kalender, S.; Ogutcu, A.; Uzunhisarcikli, M.; Kalender, Y., Malathion-induced oxidative stress in human erythrocytes and the protective effect of vitamins C and E in vitro. Environmental toxicology 2009, 24, 235-242. 41. Ranjbar, A.; Ghahremani, M. H.; Sharifzadeh, M.; Golestani, A.; Ghazi-Khansari, M.; Baeeri, M.; Abdollahi, M., Protection by pentoxifylline of malathion-induced toxic stress and mitochondrial damage in rat brain. Human & experimental toxicology 2010, 29, 851-864. 42. Possamai, F.; Fortunato, J.; Feier, G.; Agostinho, F.; Quevedo, J.; Wilhelm Filho, D.; Dal-Pizzol, F., Oxidative stress after acute and sub-chronic malathion intoxication in Wistar rats. Environmental toxicology and pharmacology 2007, 23, 198-204. 43. Ott, M.; Gogvadze, V.; Orrenius, S.; Zhivotovsky, B., Mitochondria, oxidative stress and cell death. Apoptosis 2007, 12, 913-922. 44. Shi, J.; Zhou, J.; Ma, H.; Guo, H.; Ni, Z.; Duan, J. a.; Tao, W.; Qian, D., An in vitro metabolomics approach to identify hepatotoxicity biomarkers in human L02 liver cells treated with pekinenal, a natural compound. Analytical and bioanalytical chemistry 2016, 408, 1413-1424. 45. Liu-Wu, Y.; Hurt-Camejo, E.; Wiklund, O., Lysophosphatidylcholine induces the production of IL-1β by human monocytes. Atherosclerosis 1998, 137, 351-357. 46. Gravaghi, C.; La Perle, K. M.; Ogrodwski, P.; Kang, J. X.; Quimby, F.; Lipkin, M.; Lamprecht, S. A., Cox-2 expression, PGE2 and cytokines production are inhibited by endogenously synthesized n-3 PUFAs in inflamed colon of fat-1 mice. The Journal of nutritional biochemistry 2011, 22, 360-365. 47. Makarov, S. S., NF-κB as a therapeutic target in chronic inflammation: recent advances. Molecular medicine today 2000, 6, 441-448. 48. Lee, K. M.; Kang, B. S.; Lee, H. L.; Son, S. J.; Hwang, S. H.; Kim, D. S.; Park, J. S.; Cho, H. J., Spinal NF-kB activation induces COX-2 upregulation and contributes to inflammatory pain hypersensitivity. European Journal of Neuroscience 2004, 19, 3375-3381. 49. Lasram, M. M.; Dhouib, I. B.; Bouzid, K.; Lamine, A. J.; Annabi, A.; Belhadjhmida, N.; Ahmed, M. B.; El Fazaa, S.; Abdelmoula, J.; Gharbi, N., Association of inflammatory response and oxidative injury in the pathogenesis of liver steatosis and insulin resistance following subchronic exposure to malathion in rats. Environmental toxicology and pharmacology 2014, 38, 542-553. 50. Simon, H. U.; Haj-Yehia, A.; Levi-Schaffer, F., Role of reactive oxygen species (ROS) in apoptosis induction. Apoptosis 2000, 5, 415-418. 51. Circu, M. L.; Aw, T. Y., Reactive oxygen species, cellular redox systems, and apoptosis. Free Radical Biology and Medicine 2010, 48, 749-762. 52. Reddy, B. S., Omega-3 fatty acids in colorectal cancer prevention. International journal of cancer 2004, 112, 1-7. 53. Tan, Y. Z.; Huang, W. G.; Chen, F. Y.; Li, J.; Zhou, J. Y.; Wang, L. J.; Chen, L.; Zhu, H. L., n-3 Polyunsaturated fatty acids enhance the antitumor effect of 5-fluorouracil by inhibiting bcl-2 and mutant-p53. European Journal of Lipid Science and Technology 2013, 115, 1483-1491. 54. Reed, J. C., Bcl-2 and the regulation of programmed cell death. The Journal of cell biology 1994, 124, 1-6. 55. Kaufman, C. K.; Fuchs, E., It's got you covered: NF-κB in the epidermis. The Journal of cell biology 2000, 149, 999-1004.
ACS Paragon Plus Environment
Page 28 of 32
Journal of Agricultural and Food Chemistry
Mortality rate%
100
R-(+)-MA S-(-)-MA rac-MA MO
80 60 40 20 0 0
200
400
600
800
1000
660 661 662 663 664
665 666 667 668
100
50
0 co
concentration/μM
150
nt r M ol A M -5 A M -5 A- 0 1 M 00 O M -5 O R- MO -50 R- (+)- -100 R- (+)- MA (+ M -5 )-M AS - A - 50 S- (-)-M100 S- (-)-M A(-) A 5 -M -5 A- 0 10 0
B
A
Viability(% of control condition)
Page 29 of 32
Fig. 1 A. Mortality rate of HepG2 cells induced by different concentrations of rac-malathion, R-(+)malathion, S-(-)-malathion, and malaoxon for 48 h. B. Effects of 5, 50, and 100 μM rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon on cell viability of HepG2 cells for 48 h.
Fig. 2. PLS-DA score plots based on Q-TOF data sets of HepG2 cells treated with three doses of malathion racemate, enantiomers, and malaoxon. (A) Positive mode of 5 μM exposure (R2X = 0.326, Q2 = 0.326); (B) negative mode of 5 μM exposure, (R2X = 0.614, Q2 = 0.544); (C) positive mode
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
669 670 671 672 673
674 675 676 677
of 50 μM exposure (R2X = 0.399, Q2 = 0.401); (D) negative mode of 50 μM exposure, (R2X = 0.597, Q2 = 0.495); (E) positive mode of 100 μM exposure (R2X = 0.435, Q2 = 0.543); (F) negative mode of 100 μM exposure, (R2X = 0.619, Q2 = 0.475).
Fig. 3. Numbers of changed HepG2 cells endogenous metabolites after exposure to (A) racmalathion, R-(+)-malathion, and S-(-)-malathion; (B) rac-malathion and malaoxon.
678 679 680 681 682
Fig. 4. Global metabolic pathways affected by the four malathion compounds based on MetaboAnalyst 3.6. (A) rac-malathion; (B) R-(+)-malathion; (C) S-(-)-malathion; (D) malaoxon. The following abbreviations were used: a. Glycerophospholipid metabolism; b. Arginine and proline metabolism; c. Alanine, aspartate, and glutamate metabolism; d. Arachidonic acid
ACS Paragon Plus Environment
Page 30 of 32
Page 31 of 32
metabolism; e. Pantothenate and CoA biosynthesis; f. Phenylalanine metabolism; g. Lysine degradation; h. Aminoacyl-tRNA biosynthesis; i. Glutamine and glutamate metabolism; j. Lysine biosynthesis; k. Taurine and hypotaurine metabolism; l. Glycine, serine, and threonine metabolism; m. Histidine metabolism. MA
MO ck MA-5 MA-50 MA-100
15000
* ** *
**
5000
** ** *
*
M
10000 ** ** **
0
* *
R-(+)-MA
8000
M
*
et
Se r Th r A sn
M
0 Le u G ln M et
2000
0
ln
**
2000
Se r Th r A sn G ly A la H is Ly s Pr o A sp G lu Va l Ph e
** **
4000
G
*
6000
ly A la H is Ly s Pr o A sp G lu Va l Ph e
*
**
G
*
6000
ck R-(+)-MA-5 R-(+)-MA-50 R-(+)-MA-100
10000
ck S-(-)-MA-5 S-(-)-MA-50 S-(-)-MA-100
*
Le u G ln M et
sn G ly A la H is Ly s Pr o A sp G lu Va l Ph e
Th r
Se r
u G ln M et
Le
sn G ly A la H is Ly s Pr o A sp G lu Va l Ph e
r
r
Se
Th
A
S-(-)-MA
** ** **
8000
M
**
0
10000
4000
** **
5000
*
*
ck MO-5 MO-50 MO-100
** **
A
M
10000
15000
Le u
683 684 685 686
Journal of Agricultural and Food Chemistry
687 Fig. 5 Effects on HepG2 cells amino acid levels induced by 5, 50, and 100 μM rac-malathion, R(+)-malathion, S-(-)-malathion, and malaoxon for 48 h. (* P < 0.05, **P < 0.01 compared to the control group).
SOD
CAT
** * 50
** **
** 0
5
0
10 0
50
5
0
*
5
**
** **
0
concentration/μM
concentration/μM
concentration/μM
Fig. 6 Effects of 5, 50, and 100 μM rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon on the activity of antioxidant enzymes and intracellular concentration of reduced glutathione. (* P < 0.05, **P < 0.01 compared to the control group). NF-KB
COX-2 2.0
2.5
*
*
*
**
** * *
1.0 0.5
** *
1.5
*
** ** * *
** ** ** ** **
1.0
rac-MA MO R-(+)-MA S-(-)-MA
0.5
0 10
50
10 0
50
5
0
concentration/μM
5
0.0
0.0
0
fold change
* *
1.5
**
fold change
**
2.0
697
10
10 0
0
692
696
**
**
10 0
5
100
rac-MA MO R-(+)-MA S-(-)-MA
15
50
**
**
5
*
20
mgGSH/gprot
*
U/mgprot
U/mgprot
10
0
693 694 695
GSH
150
15
50
688 689 690 691
concentration/μM
Fig. 7 Effects on mRNA levels of inflammatory cascade gene in HepG2 cells treated with 5, 50, and
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
100 μM rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon for 48 h. (* P < 0.05, **P < 0.01 compared to the control group). Caspase 3
Caspase 9
705 706 707 708 709 710 711 712 713
1.0
0.5
fold change
0.5
fold change
1.0
1.0
** **
0.5
**
1.5
** **
** **
**
rac-MA MO R-(+)-MA S-(-)-MA
1.0 0.5
concentration/μM
10 0
50
0
10 0
50
5
0
0 10
50
concentration/μM
5
0.0
0.0 0
0 10
50
5
0.0 0
701 702 703 704
2.5
1.5
2.0
1.5
0.0
700
bcl-2
bax
1.5
fold change
fold change
2.0
5
698 699
Page 32 of 32
concentration/μM
concentration/μM
Fig. 8 Effects on mRNA levels of apoptotic genes in HepG2 cells treated with 5, 50, and 100 μM rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon for 48 h. (* P < 0.05, **P < 0.01 compared to the control group).
Fig. 9 Effects on protein content in HepG2 cells treated with 100 μM rac-malathion, R-(+)malathion, S-(-)-malathion, and malaoxon for 48 h. β-actin was used as the internal standard. (* P < 0.05, **P < 0.01 compared to the control group).
Table 1. Cytotoxicity of rac-malathion, R-(+)-malathion, S-(-)-malathion, and malaoxon to HepG2 cells for 48 h.
Compounds
EC50
R2
rac-Malathion R-(+)-Malathion S-(-)-Malathion Malaoxon
694.8+65.2 815.9+91.4 547.6+47.5 832.7+80.6
0.950 0.920 0.953
714 715
ACS Paragon Plus Environment
0.971