Journal Pre-proof Deltamethrin induces liver fibrosis in quails via activation of the TGF-β1/Smad signaling pathway Bing Han, Zhanjun Lv, Xiaoya Zhang, Yueying Lv, Siyu Li, Pengfei Wu, Qingyue Yang, Jiayi Li, Bing Qu, Zhigang Zhang PII:
S0269-7491(19)35178-4
DOI:
https://doi.org/10.1016/j.envpol.2019.113870
Reference:
ENPO 113870
To appear in:
Environmental Pollution
Received Date: 12 September 2019 Revised Date:
20 December 2019
Accepted Date: 20 December 2019
Please cite this article as: Han, B., Lv, Z., Zhang, X., Lv, Y., Li, S., Wu, P., Yang, Q., Li, J., Qu, B., Zhang, Z., Deltamethrin induces liver fibrosis in quails via activation of the TGF-β1/Smad signaling pathway, Environmental Pollution (2020), doi: https://doi.org/10.1016/j.envpol.2019.113870. This is a PDF file of an article that has undergone enhancements after acceptance, such as the addition of a cover page and metadata, and formatting for readability, but it is not yet the definitive version of record. This version will undergo additional copyediting, typesetting and review before it is published in its final form, but we are providing this version to give early visibility of the article. Please note that, during the production process, errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain. © 2019 Published by Elsevier Ltd.
1
Deltamethrin induces liver fibrosis in quails via activation of
2
the TGF-β1/Smad signaling pathway
3
Bing Han a, Zhanjun Lv a,b, Xiaoya Zhang a, Yueying Lv a, Siyu Li a, Pengfei Wu a,
4 5
Qingyue Yang a, Jiayi Li a, Bing Qu a, Zhigang Zhang a,b,* a
College of Veterinary Medicine, Northeast Agricultural University, Harbin, 150030,
6 7
China b
Heilongjiang Key Laboratory for Laboratory Animals and Comparative Medicine,
8 9 10
Harbin, 150030, China * Corresponding author. E-mail address:
[email protected] (Z.G. Zhang).
11 12
ABSTRACT
13
Deltamethrin (DLM) is an important member of the pyrethroid pesticide family, and
14
its widespread use has led to serious environmental and health problems. Exposure to
15
DLM causes pathological changes in the liver of animals and humans and can lead to
16
liver fibrosis. However, the mechanism of DLM-induced liver fibrosis remains
17
unclear. Therefore, to address its potential molecular mechanisms, we used both in
18
vivo and in vitro methods. Quails were treated in vivo by intragastric administration of
19
different concentrations of DLM (0, 15, 30, or 45 mg kg-1), and the chicken liver
20
cancer cell line LMH was treated in vitro with various doses of DLM (0, 50, 200, or
21
800 µg mL-1). We found that DLM treatment in vivo induced liver fibrosis in a
22
dose-dependent manner through the promotion of oxidative stress, activation of 1
23
transforming growth factor-β1 (TGF-β1) and phosphorylation of Smad2/3. Treatment
24
of LMH cells with different concentrations of DLM similarly induced oxidative stress
25
and also decreased cell viability. Collectively, our study demonstrates that
26
DLM-induced liver fibrosis in quails occurs via activation of the TGF-β1/Smad
27
signaling pathway.
28 29
Keywords: Deltamethrin; Liver; Oxidative stress; Fibrosis; TGF-β1/Smad
30 31
Deltamethrin induces liver fibrosis in quails via activation of the TGF-β1/Smad
32
signaling pathway
33 34
1. Introduction
35
Insecticides have been used in agriculture for centuries and have had a major
36
impact on improving agricultural productivity (Kurek et al., 2017). The use of
37
pyrethroid insecticides has increased significantly since the implementation of
38
restrictions on organophosphates, and over the past two decades, pyrethroids have
39
become the preferred pesticide in many agricultural countries (Kumar et al., 2016). As
40
an important member of the pyrethroid family, deltamethrin (DLM) is a
41
broad-spectrum insecticide that can be used for pest prevention in agriculture (Milam
42
et al., 2000), as well as insecticidal and parasitic control of poultry (Zeman and
43
Železny, 1985; Soderlund et al., 2002; Khater et al., 2013). Compared with similar
44
pesticides in its class, DLM is the most frequently used. Consequently, its residues on 2
45
crops and its accumulation in water have led to serious environmental pollution, as
46
well as health problems for humans and many animals, including aquatic organisms
47
(Abdel-Daim et al., 2014; Abdelkhalek Nevien et al., 2015). Direct contact with DLM
48
vapors or consumption of DLM-contaminated food and water is the most common
49
route of poisoning (Barlow et al., 2001). DLM induces a variety of pathological
50
changes, including the inhibition of mitosis and chromosomal aberrations (Agarwal et
51
al., 1994), as well as histological changes in some vital organs, such as liver (Shona et
52
al., 2010; Arora et al., 2016).
53
Liver is the main site for the metabolism and detoxification of exogenous chemicals
54
(e.g., pesticides, drugs, and metals), and exposure to DLM has been reported to lead
55
to pathological changes in liver (Toś-Luty et al., 2001; Dubey et al., 2013; Xu et al.,
56
2015). DLM-induced hepatotoxicity can occur by a variety of mechanisms, such as
57
free radical production, lipid peroxidation, inflammation, and apoptosis (Khater et al.,
58
2013; Anoop et al., 2015). Liver fibrosis is a response to wound healing during
59
chronic liver injury and results in scarring of the tissue. Repetitive or long-term injury
60
causes excessive accumulation of scar tissue and eventually, leads to cirrhosis and
61
liver cancer. Liver fibrosis is a widespread health problem, with global deaths caused
62
by cirrhosis and primary liver cancer at approximately 1.4 million per year (Liteplo et
63
al., 2002). However, no studies to date have addressed the mechanism by which DLM
64
induces liver fibrosis.
65
In several liver diseases, oxidative stress is the major cause of liver damage.
66
Studies have shown that DLM poisoning leads to an imbalance in homeostasis and 3
67
causes oxidative stress (Dinu et al., 2010), which promotes inflammation and
68
apoptosis (Liu et al., 2018; Tan et al., 2018; Li et al., 2019b). Transforming growth
69
factor-β1 (TGF-β1) is one of the most potent factors in promoting liver fibrosis and
70
plays a key role in the occurrence and maintenance of fibrosis (Cui et al., 2003;
71
Schuppan et al., 2003; Wells et al., 2004; Liu et al., 2010). Oxidative stress can also
72
enhance the levels of TGF-β1 (Meng et al., 2019; Rashid et al., 2019). The profibrotic
73
effect of TGF-β1 is extensive and complex, and the most important pathway in the
74
development of fibrosis is the TGF-β1/Smad signaling pathway (Yao et al., 2018; Liu
75
et al., 2019a; Liu et al., 2019b).
76
Quail (Coturnix coturnix) is a popular avian model species commonly used for
77
toxicity testing and assessment of pesticide safety. Quail is also a source of food for
78
humans. DLM enters and accumulates in the body of the quail, posing a potential
79
threat to human health. Therefore, our study investigated DLM-induced liver fibrosis
80
and its potential molecular mechanism.
81
2. Materials and methods
82
2.1. Reagents and antibodies
83
DLM (25 mg mL-1) was purchased from Nanjing Red Sun Co., Ltd. (Nanjing,
84
China). Assay kits for superoxide dismutase (SOD), malondialdehyde (MDA),
85
glutathione (GSH), and hydroxyproline (HYP) were obtained from Jiancheng
86
Bioengineering Institute (Nanjing, China). Kits for CCK-8 and ROS detection, protein
87
extraction, bicinchoninic acid protein assay, as well as phenylmethylsulfonyl fluoride
88
and radio immunoprecipitation assay lysis buffer were obtained from Beyotime 4
89
Biotechnology (Shanghai, China). TRIzol was purchased from Ambion (Foster City,
90
CA, USA), a cDNA synthesis kit was purchased from Vazyme Biotech Co., Ltd
91
(Nanjing, China), and 2X PCR Taq Plus Master Mix with dye was purchased from
92
Applied Biological Materials (Vancouver, Canada). DNA markers were purchased
93
from Tiangen Biotech Co., Ltd. (Beijing, China). Antibodies to collagen-Ι (Col-Ι),
94
alpha-smooth muscle actin (α-SMA), phospho-Smad2, Smad2, phospho-Smad3, and
95
Smad3 were obtained from Bioss Biotechnology (Beijing, China). All secondary
96
antibodies were purchased from ZSGB-BIO (Beijing, China). An antibody to
97
glyceraldehyde-3-phosphate dehydrogenase (GAPDH) was obtained from Hangzhou
98
Goodhere Biotechnology (Hangzhou, China).
99
2.2. Animals and treatments
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Healthy male quails (21 days old, weighing 80 ± 15 g) were purchased from the
101
Wanjia poultry farm (Heilongjiang, China) and were acclimated for one week before
102
the start of the experiment. The quails were maintained under specific pathogen-free
103
conditions on a 12 h light/12 h dark cycle, at a room temperature of 22 ± 2 °C and
104
relative humidity of 55 ± 5%. Food and water were provided ad libitum. The animal
105
study was conducted according to the Ethical Committee for Animal Experiments of
106
Northeast Agricultural University. Quails were randomly distributed into four groups
107
(n = 10 per group) and given 0.9% (w/v) saline as a control or different doses of DLM
108
(15, 30, 45 mg kg-1) by intragastric administration. All treatments were given daily for
109
a total of 12 weeks, and 24 hours after the last administration, the quails were
110
sacrificed. Livers were immediately removed, frozen in liquid nitrogen, and stored at 5
111
–80 °C until the time of analysis.
112
2.3. Biochemical analysis
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Quail blood was collected and centrifuged at 3000 rpm for 10 min. The activities of
114
alanine aminotransferase (ALT) and aspartate aminotransferase (AST), and the
115
concentrations of triglyceride (TG) and total cholesterol (TC) in serum were measured
116
using a Beckman DXC 800 biochemical analyzer (Kong et al., 2019; Lv et al., 2020a;
117
Yang et al., 2019).
118
Liver tissue was homogenized in phosphate-buffered saline (pH 7.4) for 10 min
119
using an Ultra-Turrax T25 Homogenizer and then centrifuged at 2500 rpm for 10 min
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at 4 °C. SOD activity and the concentration of MDA and GSH in the supernatant were
121
assessed using commercially available kits.
122
Liver HYP content was measured by an alkaline hydrolysis method, following the
123
manufacturer’s instructions. Liver tissue was hydrolyzed, and the pH was adjusted to
124
6.0-6.8. The samples were then centrifuged at 3500 rpm for 10 min at 4 °C, and the
125
absorbance at 550 nm was measured in a microplate reader (BioTek Epoch, Vermont,
126
USA).
127
2.4. Quantitative reverse-transcription PCR
128
Total RNA was extracted from liver tissue using TRIzol reagent, and cDNA was
129
synthesized using a High Capacity cDNA Reverse Transcription kit. The
130
concentration of purified RNA was determined by UV spectrum at 260 nm (Zhu et al.,
131
2019). Quantitative reverse-transcription PCR (RT-qPCR) was performed using a
132
SYBR Green RT-qPCR SuperMix kit with gene specific primers (shown in Table 1) 6
133
synthesized by Sangon Biotech (Shanghai, China). Relative mRNA levels were
134
calculated by standard methods (2−∆∆Ct). (Dong et al., 2019a; Dong et al., 2019b; Han
135
et al., 2019).
136
Table 1 Primers sequences for qPCR Genebank Gene
Primer sequence (5’ → 3’) Number
β-actin
AB199913
Forward: CAGGATGCAGAAGGAGATCACAGC Reverse: GGATAGAGCCTCCGATCCAGACAG
TGF-β1
XM_015850545.1 Forward: CCGACTACTGCTTCGGGACT Reverse: TACTGTGTGTCTGCGCTCCA
ColΙ-α1
XM_015885868
Forward: CGTCGCCATCCAACTGACCTTC Reverse: TGCCAGTCTCCTCGTCCATGTAG
FN1
XM_015867978
Forward: GTGGCGAAGAAGACACTGCTGAG Reverse: AGTTGACGGTAAGGCTGGTAGGAG
α-SMA
XM_015866808
Forward: GGGATGGAATCTGCTGGCAT Reverse: GCCCGGGTACATTGTAGTGC
137
2.5. Histology
138
Liver tissue was fixed in 10% formalin, embedded in paraffin, cut into 5–6 µm
139
thick sections (Sonne et al., 2018; Li et al., 2019a), and then stained with hematoxylin
140
and eosin (HE) or Masson’s trichrome. The sections were scanned using the
141
Pannoramic MIDI slide scanner (Budapest, Hungary).
142
For transmission electron microscopy (TEM), liver tissue (about 1 mm3) was 7
143
rapidly fixed in 2.5% glutaric dialdehyde at 4 °C. After washing in 0.1 M
144
phosphate-buffered saline (PBS), the samples were fixed with 1% osmic acid,
145
dehydrated with ethanol and acetone, and then impregnated with acetone and
146
embedding solution. After embedding, the samples were cut into 50-60 nm thick
147
sections and stained with uranyl acetate and lead citrate. The sections were examined
148
by transmission electron microscopy (TEM, H-7650, Hitachi, Japan).
149
To measure lipids in the liver, tissues were fixed and dehydrated. Samples were
150
then pre-cooled in a cryostat, cut into 10 µm thick sections, and then stained with Oil
151
Red O. The sections were examined by light microscopy (Olympus BX-FM, Tokyo,
152
Japan).
153
2.6. Western blotting
154
Liver tissue was homogenized in radio immunoprecipitation assay buffer
155
supplemented with 1 mM phenylmethanesulfonyl fluoride (Li et al., 2020), and total
156
protein lysates were prepared using a protein extraction kit, following the
157
manufacturer’s instructions. Protein concentrations were determined by the
158
bicinchoninic acid method, and 5 µL samples containing 5 µg of total protein were
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resolved by SDS-PAGE and transferred to a polyvinylidene fluoride membrane for
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western blotting. Nonspecific binding to the membrane was blocked by incubation in
161
5% nonfat milk in Tris-buffered saline plus Tween 20 for 2 h at room temperature.
162
Membranes were then incubated overnight at 4 °C with the appropriate concentration
163
of protein-specific antibodies. The blots were washed in Tris-buffered saline plus
164
Tween-20, incubated with horseradish peroxidase-conjugated secondary antibodies at 8
165
37 °C for 30 min, and then washed six times with Tris-buffered saline plus Tween-20.
166
Finally, densitometry was performed using Image Pro-Plus 6.0 software (General
167
Electric Company, Fairfield, CT, USA). The experiments were repeated three times,
168
and representative results are shown. GAPDH was used as a protein loading control
169
(Lv et al., 2020b).
170
2.7. Cell culture and treatment
171
The chicken liver cancer cell line LMH was purchased from American Type
172
Culture Collection (Manassas, VA, USA) and cultured in 1640 medium containing
173
10% heat-inactivated fetal bovine serum, 100 U mL-1 penicillin, and 100 µg mL-1
174
streptomycin. The cells were maintained in a humidified 95% air/5% CO2 incubator at
175
37 °C. For experiments, after dilution of DLM with sterile PBS, the cells were treated
176
with DLM (50 µg mL-1, 200 µg mL-1, 800 µg mL-1) or sterile PBS as a control, and
177
then incubated for 24 h.
178
2.8. Cell viability and intracellular ROS assays
179
LMH cells were seeded in 96-well plates at 5×105 cells/well and treated as
180
described above for 24 h. Cell viability was determined using a CCK-8 kit, according
181
to the manufacturer’s protocol.
182
Intracellular ROS levels were measured using a 2′,7′-dichlorfluoresceindiacetate
183
(DCFH-DA) fluorescent dye assay kit according to the manufacturer’s instructions
184
(Gasparotto et al., 2013). Briefly, LMH cells were seeded in 12-well plates at 5×104
185
cells/well and cultured overnight. The cells were then treated with DLM as described
186
above. After 24 h, DCFH-DA was added to the cells in serum-free medium at a final 9
187
concentration of 10 µM, and the plates were incubated at 37 °C for an additional 20
188
min. The cells were then washed with serum-free medium. Fluorescence was
189
measured at 488 nm (excitation) and 525 nm (emission) (Cao et al., 2017; Cao et al.,
190
2019; Zhang et al., 2019) using a SpectraMax® iD3 plate reader equipped with
191
SoftMax® Pro 7 software (Molecular Devices, San Jose, CA, USA).
192
2.9. Protein–protein interaction analysis
193
Analysis of the Protein–Protein Interaction (PPI) networks of differentially
194
expressed proteins identified in this study was performed using the STRING database
195
(http://string-db.org/). We constructed networks for the species available in the
196
database by extracting target gene sequences. The networks were then built according
197
to known protein interactions in the selected reference species (rat).
198
2.10. Statistical analysis
199
All analyses were performed using SPSS 19.0 software (IBM, Armonk, NY, USA).
200
Data are expressed as the mean ± standard error (SEM). Group means were compared
201
using one-way analysis of variance (Chen et al., 2019) followed by a Tukey’s
202
post-hoc test (Sonne et al., 2017). P values of < 0.05 was considered significant.
203
3. Results
204
3.1. DLM induced pathological changes in the liver
205
To examine the effect of DLM treatment on quail liver, we first assessed tissue
206
morphology by histological staining. HE staining of the control showed normal liver
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tissue structures. However, the DLM-treated animals showed dose-dependent changes
208
in liver morphology. In the low-dose DLM group (15 mg kg-1), the structure of the 10
209
hepatocytes was altered, the hepatic cord and hepatic sinus were disordered, and
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inflammatory cells had infiltrated and aggregated in the liver. The changes caused by
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DLM treatment in the middle-dose DLM group (30 mg kg-1) were similar to those in
212
the low-dose DLM group, but slightly more severe. The morphology of the liver in
213
the high-dose DLM group (45 mg kg-1) was altered dramatically. The hepatic cord
214
and hepatic sinus were severely disordered, and the hepatocytes were swollen and
215
some had ruptured. The marginal hepatocytes appeared flaky and necrotic, and a large
216
number of fat vacuoles were present and scattered throughout the tissue. There was
217
also a large number of inflammatory cells present in the liver (Fig. 1).
218
Transmission electron microscopy of liver tissue showed that compared with the
219
control group, the morphology of hepatocytes in the low-dose DLM group (15 mg
220
kg-1) was altered. The nuclei were not obvious, and some mitochondrial cristae were
221
broken. The morphology of hepatocytes in the middle-dose DLM group (30 mg kg-1)
222
were similar, but more severe than those in the low-dose DLM group. The
223
morphology of the hepatocytes in the high-dose DLM group (45 mg kg-1) showed
224
significant changes in structure, including a large number of lipid droplets around the
225
nucleus and mitochondrial degeneration, with swelling and loss of mitochondrial
226
structure. Mitochondrial cristae were severely broken or missing, and some
227
mitochondrial vacuolization was observed (Fig. 1).
228
3.2. DLM induced an increase in the activity of liver biomarkers
229
ALT and AST are commonly used biomarkers for liver damage. Compared with
230
the control group, DLM administration significantly increased ALT and AST 11
231
activities in a dose-dependent manner (Fig. 2A and 2B).
232
3.3. DLM induced oxidative stress in the liver
233
To examine whether DLM treatment induced oxidative stress in the liver, we
234
measured several markers, including MDA, GSH, and SOD. As shown in Figure 2,
235
DLM administration significantly increased MDA concentration (Fig. 2C), reduced
236
GSH levels (Fig. 2D), and decreased SOD activity (Fig. 2E) in the liver in a
237
dose-dependent manner.
238
3.4. DLM decreased cell viability and increases ROS levels in LMH cells
239
To test the effect of DLM in vitro, we treated LMH cells with different
240
concentrations of DLM. We found that the growth of LMH cells was significantly
241
inhibited by DLM treatment, as measured by the CCK-8 cell proliferation assay (Fig.
242
3A).
243
To assess oxidative stress in the DLM-treated LMH cells, we measured the
244
concentration of intracellular ROS. The results showed that treatment with DLM
245
significantly increased ROS levels (Fig. 3B).
246
3.5. DLM induced steatosis in the liver
247
Steatosis is another indicator of liver damage. To determine whether DLM causes
248
steatosis, we measured lipid levels in the DLM-treated quails. As shown in Figure 4,
249
DLM administration significantly increased TG and TC concentrations, and this effect
250
was dose-dependent. The results of Oil Red O staining showed that there were
251
multiple areas of lipid accumulation in the DLM-treated groups, and these were
252
significantly increased compared with the control group. 12
253
3.6. DLM induced fibrosis in the liver
254
Damage to the liver leads to fibrosis, which is the formation and accumulation of
255
scar tissue and primarily composed of the protein collagen. HYP is the main
256
component of collagen and a good indicator of collagen levels. As shown in Figure
257
5A, we measured HYP levels and found that they were significantly higher in the
258
liver of DLM-treated quails compared with the control group, and this effect was
259
dose-dependent. Histological staining with Masson’s trichrome, which also measures
260
collagen levels, showed that collagen fibers increased significantly in the hepatic
261
sinusoids in a dose-dependent manner in the DLM groups (Fig. 5B).
262
3.7. DLM induced liver fibrosis via the TGF-β1/Smad signaling pathway
263
The livers of DLM-treated quails contained significantly higher levels of the Col-Ι,
264
α-SMA, p-Smad2, and p-Smad3 proteins, and this occurred in a dose-dependent
265
manner compared with the control group (Fig. 6A and 6B).
266
RT-qPCR analysis showed that mRNA levels of α-SMA, ColΙ-α1, FN1, and
267
TGF-β1 in the DLM groups were significantly increased in a dose-dependent manner
268
compared with the control group (Fig. 6E).
269
3.8. PPI analysis
270
To confirm our findings, we constructed a PPI network of fibrosis related genes
271
using the STRING 10 database (Fig. 7). The dynamic clusters for fibrosis included
272
TGF-β1, ColΙ-α1, FN1, Smad2, and Smad3. These functional interaction networks
273
revealed a link between fibrosis and the TGF-β1/Smad signaling pathway.
274
4. Discussion 13
275
Because of the widespread use of DLM as an insecticide, its impact on the
276
environment and human health has become an ever-increasing issue (Sibiya et al.,
277
2019). Exposure to DLM has been shown to cause histological changes in several
278
vital organs (Shona et al., 2010). Many studies have shown that in young and adult
279
rats, DLM is found in plasma and accumulates in multiple tissues, including brain,
280
liver, fat, and muscle (Berkowitz et al., 2003; Morgan et al., 2007; Kim et al., 2010;
281
Naeher et al., 2010). Moreover, DLM can lead to excessive ROS production in rat
282
liver, kidney, and brain, thereby inducing oxidative stress (Abdou and Abdel-Daim,
283
2014; Abdel-Daim et al., 2014; Abdel-Daim et al., 2016). In addition, DLM has been
284
shown to induce oxidative stress in freshwater Nile tilapia, causing damage to the
285
body (Abdel-Daim et al., 2015; Abdelkhalek Nevien et al., 2015). These results are
286
consistent with our investigation of DLM induced hepatic fibrosis in quails.
287
The liver enzymes, AST and ALT, are important biochemical markers for liver
288
dysfunction and liver damage (Sonne et al., 2008; Abdel-Daim et al., 2016). In our
289
study, the increase in the activities of AST and ALT in serum reveals a loss of
290
functional integrity of the hepatocyte membrane and liver dysfunction.
291
Pesticide poisoning causes oxidative stress by producing excess free radicals or
292
ROS (Singh and Prasad, 2018) and inducing lipid peroxidation in tissues in mammals
293
and other organisms (Mansour and Mossa, 2009; Liu et al., 2017a; Baiyun et al.,
294
2018). ROS are involved in the toxic effect of pyrethroid insecticides (Mossa et al.,
295
2013), and oxidative stress is the main cause of liver damage (Yang et al., 2017;
296
Zhang et al., 2017). MDA is a product of lipid peroxidation and has been widely used 14
297
as a marker for oxidative stress (Lu et al., 2018; Wei et al., 2018; Li et al., 2019c).
298
GSH is an antioxidant that prevents cell damage caused by ROS. All cells in the
299
human body are capable of synthesizing GSH, which has been shown to be essential
300
for protection against oxidative stress (Pompella et al., 2003; Yang et al., 2016a). A
301
decrease in SOD activity can lead to the accumulation of peroxides, which also leads
302
to oxidative stress (Dinu et al., 2010; Su et al., 2019). Our results indicate that
303
oxidative stress is a key factor in the liver damage caused by DLM.
304
TG and TC are major lipids and good indicators of lipid accumulation (Liu et al.,
305
2017b; Cui et al., 2019). As the central site for lipid synthesis and utilization, the liver
306
is the main organ regulating lipid metabolism (Mio and Bloomston, 2016). Steatosis
307
can exacerbate liver damage caused by oxidative stress (Rouvinen-Watt et al., 2014;
308
Amuno et al., 2018), and once hepatic steatosis is established, inflammation,
309
mitochondrial dysfunction, and ROS-induced oxidative stress are enhanced. Lipid
310
peroxidation occurs and adipokines are produced, which can lead to further
311
hepatocyte damage and fibrosis (Day and James, 1998). Hepatic fibrosis is
312
characterized by excessive deposition of extracellular matrix (ECM) proteins, within
313
parenchymal and non-parenchymal hepatocytes, and infiltrating immune cells (Toosi,
314
2015; van Dijk et al., 2015; Baiocchini et al., 2016). The main components of ECM
315
are Col-I and FN1, and HYP is an amino acid unique to collagen. Oxidative stress has
316
also been reported to play a major role in liver fibrosis (Novo et al., 2014). In this
317
study, the oxidative stress associated with liver fibrosis is caused by increased ROS
318
and decreased antioxidant capacity. This appears to induce hepatic stellate cell (HSC) 15
319
proliferation and collagen synthesis, thereby promoting liver fibrosis in quails.
320
TGF-β1 is the most potent factor in promoting liver fibrosis and plays a key role in
321
its occurrence and maintenance (Cui et al., 2003; Schuppan et al., 2003; Wells et al.,
322
2004; Liu et al., 2010). TGF-β1 strongly stimulates HSC to produce Col-Ι and Col-III,
323
thereby producing a large amount of ECM and inhibiting ECM degradation (Yang et
324
al., 2016b). TGF-β1 also binds to receptors on the cell membrane, phosphorylating
325
the receptor-associated Smad2/3 proteins. The conformational changes of activated
326
Smad2/3 results in its release from the receptor complex, which, in turn, leads to
327
interaction with Smad4 to form the Smad2/3-Smad4 complex (Ma et al., 2017). The
328
transport of this complex into the nucleus enhances the expression of α-SMA and
329
Col-Ι and promotes fibrosis. Our data are completely consistent with these events and
330
suggest that long-term exposure to DLM induces oxidative stress in the liver, thereby
331
activating the TGF-β1/Smad pathway and resulting in liver fibrosis in quail.
332
5. Conclusion
333
We discovered in quails that DLM induced liver fibrosis occurs via activation of
334
the TGF-β1/Smad pathway (Figure 8). Inhibition of TGF-β1 production may therefore
335
be a potential therapeutic target for the treatment of DLM-induced liver fibrosis.
336
Declaration of Competing Interest
337 338
The authors declare no conflict of interest.
Acknowledgement
339
This work was funded by the National Natural Science Foundation of China
340
(31972754), Scientific Research Foundation for the Returned Overseas Chinese 16
341 342
Scholars of Heilongjiang Province (LC2017007). We
thank
Kathy
Tamai,
from
Liwen
Bianji,
Edanz
Group
China
343
(www.liwenbianji.cn/ac), for editing the English text of a draft of this manuscript.
344
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638 639 640 641 642 643 644 645 646 647 648 30
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Figure legends
650
Fig. 1. Morphological characteristics and ultrastructure of liver tissues in quails. (A)
651
Control group. (B) 15 mg kg-1 DLM group. (C) 30 mg kg-1 DLM group. (D) 45 mg
652
kg-1 DLM group. Red arrow: inflammatory cell infiltration. Blue arrow: hepatic cord
653
and
654
200×magnification; Ultrastructure, 10000×magnification).
655
Fig. 2. DLM dose-dependently affected the ALT and AST activity and livers
656
oxidative stress in quails. (A) The activity of ALT. (B) The activity of AST. (C) The
657
concentration of MDA. (D) The concentration of GSH. (E) The activity of SOD. Data
658
are presented as mean ± SEM (n = 10). * Statistically different (p < 0.05) VS. control
659
group.
660
Fig. 3. DLM-induced LMH cell injury and oxidative stress. (A) Cell viability (n = 6).
661
(B) The concentration of ROS. (n = 6). Data are presented as mean ± SEM. *
662
Statistically different (p < 0.05) VS. control group.
663
Fig. 4. DLM induced steatosis in the livers. (A) The concentration of TG. (B) The
664
concentration of TC. (C) Oil red O staining (200×magnification). Data are presented
665
as mean ± SEM (n = 10). * Statistically different (p < 0.05) VS. control group.
666
Fig. 5. DLM induced liver fibrosis. (A) The concentration of HYP. (B) Masson's
667
trichrome staining (200×magnification). Data are presented as mean ± SEM (n = 10).
668
* Statistically different (p < 0.05) VS. control group.
669
Fig. 6. The effect of DLM on the liver fibrosis pathway. (A) The relative protein
670
levels of Col-Ι and α-SMA. (B) The relative protein levels of p-Smad2 and p-Smad3.
hepatic
sinus
disorder.
Yellow
31
arrow:
fat
vacuole.
(HE
staining,
671
(C, D) Values of quantitative analysis (n = 4). (E) TGF-β1, FN1, α-SMA, and ColΙ-α1
672
were detected by qPCR (n = 5). Data are presented as mean ± SEM. * Statistically
673
different (p < 0.05) VS. control group.
674
Fig. 7. Protein network. Protein network of proteins regulated to fibrosis-related genes
675
expressed in rats.
676
Fig. 8. Schematic diagram of the mechanism of DLM-induced liver fibrosis in quails.
677
DLM induces liver fibrosis via activation of the TGF-β1/Smad signaling pathway.
678
32
Highlights 1. Chronic exposure of deltamethrin (DLM) induces liver fibrosis in quail. 2. DLM induces fatty degeneration of liver in quail. 3. DLM induces oxidative stress in LMH cells. 4. Oxidative stress is a key of DLM-induced liver fibrosis.
Bing Han: Conceptualization, Methodology, Validation, Data Curation, Writing-Original Draft Zhanjun Lv: Conceptualization, Writing-Original Draft, Project administration Xiaoya Zhang: Conceptualization, Methodology, Validation Yueying Lv: Validation, Formal analysis Siyu Li: Software, Formal analysis Pengfei Wu: Validation Qingyue Yang: Validation Jiayi Li: Software, Formal analysis Bing Qu: Writing-Review & Editing Zhigang Zhang: Conceptualization, Methodology, Writing-Review & Editing, Project administration
Declaration of interests ☒ The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. ☐The authors declare the following financial interests/personal relationships which may be considered as potential competing interests:
We declare that we have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.