Subscriber access provided by AUBURN UNIV AUBURN
Biotechnology and Biological Transformations
CsFEX, a fluoride export protein gene from Camellia sinensis, alleviates fluoride toxicity in transgenic Escherichia coli and Arabidopsis thaliana Jiaojiao Zhu, Anqi Xing, Zichen Wu, Jing Tao, Yuanchun Ma, Bo Wen, Xujun Zhu, Wanping Fang, and Yuhua Wang J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.9b00509 • Publication Date (Web): 06 May 2019 Downloaded from http://pubs.acs.org on May 7, 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 40
Journal of Agricultural and Food Chemistry
1
CsFEX, a fluoride export protein gene from Camellia sinensis,
2
alleviates fluoride toxicity in transgenic Escherichia coli and
3
Arabidopsis thaliana
4 5
Jiaojiao Zhu1, Anqi Xing1, Zichen Wu1, Jing Tao1, Yuanchun Ma1, Bo Wen1, Xujun Zhu1,
6
Wanping Fang1, Yuhua Wang1*
7 8
1 College
of Horticulture, Nanjing Agricultural University, Nanjing 210095, China
9 10
E-mail:
11
Jiaojiao Zhu:
[email protected] Anqi Xing:
[email protected] 12
Zichen Wu:
[email protected] Jing Tao:
[email protected] 13
Yuanchun Ma:
[email protected] Bo Wen:
[email protected] 14
Xujun Zhu:
[email protected] Wanping Fang:
[email protected] 15 16
Corresponding author
17
Yuhua Wang
18
College of Horticulture, Nanjing Agricultural University, Nanjing 210095, China
19
Tel: +86-25-84395182
20
E-mail:
[email protected] Fax: +86-25-84395182
21
1
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
22
ABSTRACT: A Fluoride export gene (CsFEX) was newly found and isolated from
23
Camellia sinensis and its functions in detoxifying F were investigated in transgenic
24
Escherichia coli and Arabidopsis thaliana. CsFEX contains two crcB domains, which
25
is the typical structure in plants. The expression of CsFEX in C. sinensis is tissue
26
specific and related to maturity of leaves, and its expression is significantly induced
27
by F treatments in different tissues of C. sinensis, particularly in leaves. Additionally,
28
the growth of C. sinensis, E. coli, and A. thaliana can all be inhibited by F treatment.
29
However, the growth of CsFEX-overexpression E. coli was increased with lower F
30
content under F treatment compared to the control. Similarly, the germination and
31
growth of CsFEX-overexpression A. thaliana were enhanced with lower F content
32
under F treatment compared to wild type. CsFEX relieves F toxicity in the transgenic
33
E. coli and A. thaliana by alleviating F accumulation.
34
KEYWORDS: Camellia sinensis, Fluoride Export Protein, F tolerance/detoxication,
35
Transgenic Escherichia coli, Transgenic Arabidopsis thaliana
2
ACS Paragon Plus Environment
Page 2 of 40
Page 3 of 40
Journal of Agricultural and Food Chemistry
36
INTRODUCTION
37
As one of the main halogens, fluorine is mainly present in the environment as
38
fluoride (F) compounds 1. With human activities 2, industrial pollution 3, and
39
application of chemical phosphate fertilizer 4, the content of F in soil has gradually
40
increased. Studies have found that F is a common phytotoxin in plants via inhibition
41
of enzyme activity
42
slowing of growth 9. Furthermore, F can be absorbed from both the soil by plant roots
43
or the air by leaves 10-11 and then transported and distributed throughout the plant 12.
5
and photosynthesis 6, resulting in the visible damage
7-8
and
44
Accumulating reports have shown that the F content of mature leaves of C.
45
sinensis is 871-1,337 mg.kg-1, while the F content of old leaves can exceed 2,000
46
mg.kg-1 13, which is 10-100 times higher than that of other plants grown in the same
47
environmental conditions
48
of F without exhibiting any toxic symptoms, indicating that C. sinensis is a
49
hyperaccumulator with high tolerance to F and has specific mechanisms driving F
50
accumulation/detoxification 17. At present, there are three mechanisms that explain the
51
accumulation and detoxification of F in C. sinensis. Cell wall precipitation and
52
vacuolar compartmentalization prevent F from entering the physiological metabolic
53
center of the protoplast without affecting the normal metabolic activities of C.
54
sinensis cells, which may be one of the mechanisms of the F tolerance observed in C.
55
sinensis
56
free aluminum 21, magnesium, calcium 10, 22-23, or tea polysaccharides allows F to exist
57
in C. sinensis in the form of stable fluoride-ligand complexes, thereby reducing F
18-20.
14-16.
Interestingly, tea seedlings accumulate large amounts
An alternative mechanism is the chelation of F ions in C. sinensis with
3
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
1, 18, 24.
58
damage to C. sinensis
Additionally, recent reports reveal that F as a signal
59
triggers the response of the defense gene (RLK) on the plasma membrane, and then
60
activates the Ca2+ ATPase, the activated Ca2+ ATPase subsequently promotes the
61
absorption and transport of F, this finding indicates that Ca2+ signaling pathway might
62
involve in F accumulation/detoxification in C. sinensis 25. However, the complicated
63
molecular mechanisms governing F accumulation/detoxification in C. sinensis remain
64
unclear.
65
Recently, many reports have indicated that the resistance to F toxicity is
66
promoted by the family of F exporters in bacteria and eukaryotes. The exporters are
67
divided into two phylogenetically unrelated categories: the first is a variant in the
68
voltage-gated chloride channel (CLC) superfamily, namely CLCF. The CLCF genes
69
encode F-/H+ antiporters in eubacteria
70
family, Fluc (formerly crcB) in bacteria 28 and FEX2 in eukaryotes 29. For example, a
71
recent study showed that FEX proteins (including FEX1 protein and FEX2 protein) in
72
Saccharomyces cerevisiae function as ion channels, that select fluorides over
73
chlorides, and FEX proteins can be constitutively expressed in yeast plasma
74
membranes
75
efflux of fluoride ions 30. Ji et al. (2014) believe that microorganisms have developed
76
into a highly selective F channel (Fluc) to cope with the presence of F stress in the
77
environment, which alleviates microbial toxicity by exporting inhibitory F in the
78
cytoplasm to outside of the cell
79
family in prokaryotes and lower eukaryotes would alleviate the damage caused by
30.
26-27.
The second is a more broadly distributed
In addition, studies have shown that FEX protein acts directly in the
31.
Nicholas et al. (2016) concluded that the Fluc
4
ACS Paragon Plus Environment
Page 4 of 40
Page 5 of 40
Journal of Agricultural and Food Chemistry
32.
80
fluorosis
Interestingly, the crcB homologs in eukaryotes (such as Neurospora
81
crassa, S. cerevisiae, and Candida albicans) play a role in the export of F, so Li et al.
82
(2013) renamed these genes as fluoride export genes (FEX), and this study directly
83
shows that FEX and Fluc are homologous genes in different organisms. Based on
84
these studies about F exporters in bacteria and eukaryotes, we speculate that F
85
exporters might also be present in C. sinensis. Nonetheless, to the best of our
86
knowledge, no F exporter gene or protein has yet been identified from C. sinensis.
87
Therefore, this study focused on identifying whether C. sinensis contains a F
88
export gene or protein, conferring its high F tolerance. Interestingly, a fragment
89
containing two crcB domains was identified from our previous reported
90
transcriptomic database (PRJNA315669) 33, named CsFEX, which encoded a putative
91
CsFEX protein. The expression of CsFEX in different tissues and different maturity of
92
C. sinensis leaves was analyzed and its response to exogenous F treatment was
93
detected in C. sinensis. Furthermore, CsFEX was cloned from C. sinensis and
94
transformed into E. coli and A. thaliana to detect the response of transgenic E. coli
95
and A. thaliana to F treatments, thereby investigating the functions of CsFEX in F
96
resistance. This study suggests that the CsFEX gene plays an important role in the F
97
tolerance in C. sinensis. To the best of our knowledge, CsFEX is an F export gene
98
which is newly found in C. sinensis in this study.
99 100
MATERIALS AND METHODS
101
Growth conditions, F treatment, and sample collection 5
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
102
The one-year-old cutting seedlings of C. sinensis cv. LongjingChangye were
103
collected from Nanjing Ya Run Tea Co., Ltd., China. The tea seedlings with uniform
104
growth were selected, rinsed with double distilled water, and used as experimental
105
materials. The seedlings were placed in three plastic containers (four C. sinensis
106
seedlings per plastic container) containing 1 L of 1/2 complete nutrient solution for 2
107
weeks in a light chamber with a photoperiod of 12-h light (25 ± 2oC)/12-hour dark (20
108
± 2oC), and 70 ± 10% relative water content. Then the seedlings were pre-cultured in
109
complete medium for 4 weeks before F treatment. The complete nutrient solution was
110
prepared following the method of Ghanati et al. (2005) 34. The nutrient solutions were
111
refreshed every 5 days, and the pH value was adjusted to 5.0 by 1 M HCl or 1 M
112
NaOH solution every day.
113
The pre-cultured C. sinensis seedlings were treated with 0 mM (control), 0.42
114
mM, and 0.84 mM NaF for 0 d, 1 d, 2 d, and 20 d. The seedlings treated by 0 or 0.84
115
mM F for 20 days were photographed to record the growth status. The young leaves
116
and new roots were collected after 2 days of treatment at 0 mM, 0.42 mM, and 0.84
117
mM F and dried at 80°C for determination of F accumulation. The young leaves (the
118
first and second leaves from the top of plants), old leaves (the first and second leaves
119
from the bottom of plants), roots, flowers, fruit, pollen, and stems of C. sinensis were
120
collected and stored at -80 °C to detect the difference in the expression of CsFEX in C.
121
sinensis. The young leaves, old leaves, roots, and stems of C. sinensis treated with
122
0.84 mM NaF for 0 d, 1 d, 2 d were collected for expression analysis. In addition, the
123
C. sinensis leaves with different maturity (buds, the first leaf, the second leaf, the third 6
ACS Paragon Plus Environment
Page 6 of 40
Page 7 of 40
Journal of Agricultural and Food Chemistry
124
leaf, the fourth leaf, the fifth leaf and the old leaf) were collected respectively for
125
expression analysis.
126 127 128
Isolation and cloning of the CsFEX gene Based on the conserved crcB domain, the CsFEX gene was detected from 33.
129
transcriptome data (PRJNA315669) reported by Pan et al. (2016)
The ORF of
130
CsFEX was acquired by amplification of PCR using the primer pairs
131
(CsFEX-ORF-F/R) listed in Table 1. The amplification product was then purified and
132
cloned into the cloning vector pDONR201 for sequencing. Subsequently, the 5' and 3'
133
untranslated region (UTR) sequences of CsFEX were amplified using the specific
134
primers CsFEX-5'GSP1/5'GSP2 and CsFEX-3'GSP1/3'GSP2 (Table 1).
135 136
Analyses of sequences and phylogenetic relationships
137
The secondary structure of the CsFEX protein was predicted using the online
138
software SOPMA (https://npsa-prabi.ibcp.fr/cgi-bin/npsa), and the model of the
139
tertiary structure of the CsFEX protein was constructed by Swiss-Model
140
(https://www.swissmodel.expasy.org). The homologous sequence was aligned by
141
DNAMAN software. A phylogenetic tree of CsFEX in C. sinensis and FEX in other
142
organisms was constructed using the neighbor-joining method in MEGA6 software.
143
The bootstrap method was used with 1,500 replicates; other parameters of the
144
phylogenetic tree were set according to Wang et al. (2016) 35.
145 7
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
146
RNA extraction, cDNA synthesis, and quantitative real-time PCR (qRT-PCR)
147
analysis
148
Total RNA of C. sinensis was extracted using a Rapid RNA Isolation Kit
149
(TaKaRa, Japan), and then the quality of RNA was assessed using the ONE DropTM
150
OD-1000+ spectrophotometer (ONE Drop, USA). cDNA was obtained with the
151
PrimeScriptTM 1st Strand cDNA Synthesis Kit (TaKaRa, Dalian, China) following the
152
manufacturer’s instructions. QRT-PCR was performed following the method reported
153
by Wang et al. (2014)
154
performed by 2−ΔΔCT method
155
CsGAPDH. All experiments were repeated three times with independent RNA
156
samples, and the primers were listed in Table 1.
36,
and the relative expression analysis of the data was 37.
The internal reference gene used in this study was
157 158
Construction of prokaryotic expression vector and F tolerance of transgenic E.
159
coli cells
160
The ORF of CsFEX was subcloned from the cloning vector pDONR201, and
161
then ligated into the pET-28a expression vector. The pET-CsFEX recombinant
162
plasmid and the empty vector were used to transform E. coli ROSETTA cells, and
163
proper insertion was confirmed by enzyme digestion and sequencing.
164
To examine the effect of overexpressing CsFEX on the growth of E. coli strains,
165
the empty vector and CsFEX transformed E. coli strains were cultured in LB medium
166
until the OD600 value reached 0.8, and then five-fold serial dilutions were inoculated
167
in solid LB media containing different concentrations of F (0 mM, 5 mM, 50 mM, and 8
ACS Paragon Plus Environment
Page 8 of 40
Page 9 of 40
Journal of Agricultural and Food Chemistry
168
100 mM), and the growth state of the two strains was observed after 12 h. Meanwhile,
169
the transformed E. coli strains with an OD600 value of 1 were added to LB liquid
170
containing different concentrations of F (0 mM, 5 mM, 50 mM, and 100 mM) at a
171
ratio of 1:1000 and then cultured in an oscillating incubator with shaking at 220 rpm
172
at 37 °C. The OD600 value was measured by a spectrophotometer at different times (2
173
h, 4 h, 8 h, 10 h, and 12 h), and the curves were plotted with GraphPad Prism software.
174
In addition, to detect the F content in the two strains, the cells were collected after
175
culturing for 10 h under treatment with different concentrations of F.
176 177
Transformation of CsFEX into A. thaliana
178
To further confirm the function of CsFEX, CsFEX was amplified using
179
CsFEX-gate-F/R (Table 1) and cloned into pDONR201. It was then recombined into
180
pK7FWG2 to generate the 35S:CsFEX:EGFP construct. Then, the construct was
181
introduced into the Colombia ecotype of A. thaliana by the floral dip method
182
Transgenic A. thaliana was screened on 1/2 MS agar media containing 50 μg·mL-1
183
kanamycin. An RT-PCR assay was conducted to verify the integration of CsFEX in
184
positive transgenic A. thaliana using gene-specific primers (CsFEX-gate-F/-R, Table
185
1), and the AtACTIN2 (AT3G18780) gene in Table 1 was used as a control. All A.
186
thaliana were grown at 22 ± 2 °C in a light incubator with a 16-h light (220
187
μmol·m−2·s−1)/8-h dark cycle.
38.
188 189
Phenotype analysis of transgenic A. thaliana and subcellular localization of 9
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
190
CsFEX
191
WT and transgenic A. thaliana seeds (WT, L-2, L-4,and L-8) were plated on
192
1/2 MS solid medium with various concentrations of F (0 mM, 4 mM, 6 mM, or 8
193
mM). After 2 days of vernalization at low temperature (4 oC), the plates were
194
transferred to a light incubator with a 16-h light (220 μmol·m−2·s−1)/8-h dark cycle for
195
7 days. The germination rate was calculated. The phenotypes of A. thaliana were
196
observed and photographed with a camera after cultured for 14 days with various
197
concentrations of F (0 mM, 4 mM, 6 mM and 8 mM). Meanwhile, A. thaliana grown
198
for 14 days on 1/2 MS solid media with different concentrations of exogenous F (4
199
mM and 6 mM) were harvested for F content detection.
200
To confirm the subcellular localization of CsFEX, signals of CsFEX-EGFP in
201
roots of WT and transgenic A. thaliana were observed by laser confocal microscopy
202
(CarlZeiss LSM710, Germany).
203 204
Extraction and determination of F in samples
205
To collect bacterial samples, the bacterial liquid was centrifuged at 5000 rpm for
206
15 min, and then resuspended 3 times with ddH2O. To collect plant samples, C.
207
sinensis and A. thaliana samples were collected and weighed. The above bacterial
208
samples and plant samples were placed into 50 mL centrifugal tubes that contained 30
209
mL of ddH2O, and then extracted at 100 °C for 30 min in water bath. The extraction
210
mixtures were cooled to room temperature and centrifuged at 5000 g for 15 min, then
211
the supernatant was collected to determine the F content using the 9609BNWP 10
ACS Paragon Plus Environment
Page 10 of 40
Page 11 of 40
Journal of Agricultural and Food Chemistry
212
fluoride ion selective electrode and 096019 stirrer probe following the description in
213
Gao et al., (2013) 39.
214 215
Statistical analyses
216
All data in this study were analyzed using SPSS version 17.0, all data were
217
presented as mean ± standard deviation (SD). Significant differences between the
218
experimental data were tested with ANOVA and Duncan’s test and were marked by
219
different letters (P < 0.05).
220 221
RESULTS
222
Accumulation of F in C. sinensis
223
The phenotype of tea seedlings was investigated after 20 days of treatment with
224
0.84 mM of F. Long-term F treatment caused the growth of tea seedlings to slow,
225
which was manifested by necrosis of new roots, chlorosis, and scorching of the young
226
leaves (Figure 1A, Figure 1B, Figure 1C and Figure 1D). Furthermore, the effects of
227
different concentrations of F on the accumulation of F in new roots and young leaves
228
(the first leaf and the second leaf) were also investigated. The results showed the F
229
content of new roots and young leaves of C. sinensis in fluorine-free culture medium
230
was 6.71 mg.kg-1 and 315.85 mg.kg-1, respectively. Then it increased to 241.97
231
mg.kg-1 and 335.45 mg.kg-1 after treated with 0.42 mM F for 2 days. It reached to
232
427.57 mg.kg-1 and 356.45 mg.kg-1 after treated with 0.84 mM F for 2 days. These
233
results indicate that the F content of young leaves and new roots of C. sinensis 11
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
234
increased significantly after 2 days of F treatment; the increase in F content in new
235
roots was significantly greater than that of young leaves (Figure 1E).
236 237
Cloning and characterization of CsFEX
238
The full-length of the CsFEX cDNA sequence is 2,205 bp (Figure 2), which
239
contains a 1,443-bp open reading frame (ORF) (Figure 3), encodes 480 amino acids
240
(predicted molecular weight 52.391 kDa), and has a theoretical isoelectric point of 6.5.
241
Through SOPMA prediction, CsFEX is composed of 38.96% α-helices, 15.21% of the
242
extended backbone, 4.79% of β-sheets, and 41.04% of random coils. The tertiary
243
results of FEX protein are presented in Figure S1. The blast alignment showed that
244
the sequence of CsFEX exhibits a high homology to FEX in plants. The phylogenetic
245
analysis of FEX in the organism showed that FEXs are mainly divided into two
246
categories, and the evolutionary relationship of FEXs between C. sinensis and other
247
plants is very close (Figure 4A). Sequence analysis by Pfam showed that FEXs in C.
248
sinensis, Actindia chinensis, Ipomoea nil, and Sesamum indicum contain two
249
conserved crcB-like protein structures (Figure 4B), which is the typical structure in
250
plants.
251 252
Expression analysis of CsFEX in C. sinensis
253
To test the expression profile of CsFEX in C. sinensis, the expression levels of CsFEX
254
were compared in roots, stems, young leaves, old leaves, fruits, flowers and pollen,
255
and the results showed that the expression level of CsFEX in the pollen and young 12
ACS Paragon Plus Environment
Page 12 of 40
Page 13 of 40
Journal of Agricultural and Food Chemistry
256
leaves of C. sinensis was significantly higher than that of other organs (Figure 5A),
257
which indicates that the expression of CsFEX in C. sinensis is tissue specific.
258
Furthermore, as shown in Figure 5B, the expression of CsFEX in different tissues of C.
259
sinensis under F treatment was increased with the increase of F treatment time. The
260
CsFEX expression level increased 7.93-fold in the young leaves of C. sinensis in
261
response to 0.84 mM F for 2 days compared to plants grown under the control
262
conditions, and the CsFEX expression levels of other organs also had slightly
263
increased after F treatment (Figure 5B). Moreover, the expression profiles of CsFEX
264
in C. sinensis leaves (bud, 1st, 2nd, 3rd, 4th, 5th and old) with different maturity was
265
detected and the results showed that the relative expression level of CsFEX was
266
lowest in the buds and first leaf, peaked in the second leaf and then it decreased with
267
the increase of leaf maturity (Figure 5C), indicating that the expression of CsFEX in C.
268
sinensis is related to the leaf maturity.
269 270
Enhanced F tolerance in E. coli cells overexpressing CsFEX
271
Reverse transcription polymerase chain reaction (RT-PCR) was performed to
272
obtain the correct overexpressed CsFEX strain and empty vector strain (Figure S2).
273
The growth of both control and overexpressing strains were inhibited by F treatment
274
in a dose-dependent manner. Furthermore, the strain overexpressing CsFEX showed
275
better growth after treatment with 0 mM, 5 mM, 50 mM, and 100 mM F compared to
276
the control (Figure 6A). Simultaneously, the results also showed that the strain
277
overexpressing CsFEX had a higher survival rate when treated with 5 mM, 50 mM, 13
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
278
and 100 mM F compared to the empty vector (Figure 6B). In addition, the results
279
showed that the strain overexpressing CsFEX accumulated lower levels of F than the
280
control, indicating that CsFEX functions in enhancing the tolerance of E. coli to F
281
(Figure 7).
282 283
Enhanced F tolerance in A. thaliana overexpressing CsFEX
284
As a C. sinensis transgenic system is currently difficult to establish, the model
285
plant A. thaliana was employed to overexpress CsFEX to further study its biological
286
functions in the accumulation of F. As shown in Figure 8A, CsFEX overexpression
287
was detected in transgenic A. thaliana lines (L-2, L-4, and L-8), but not in wild type
288
(WT) A. thaliana. The germination rate, growth status and F accumulation of WT and
289
transgenic lines were detected to investigate whether overexpression of CsFEX in A.
290
thaliana can enhance the tolerance to F stress. The germination rate of WT, L-2, L-4
291
and L-8 all approached 100% under normal conditions, and the germination rate of
292
wild and overexpressed lines were both inhibited by F treatment in a dose-dependant
293
manner. Moreover, the germination rate was higher in transgenic lines than the WT
294
under the same concentration of F treatment. For example, the germination rates of
295
L-2, L-4 and L-8 were 3.79, 6.05 and 6.87 times that of the WT under 8 mM F,
296
respectively (Figure 8B). The growth rate of wild-type and overexpressing A. thaliana
297
was significantly inhibited by exogenous F treatment, and the reduction of growth rate
298
of the WT was more severe than transgenic A. thaliana (Figure 8C). Additionally, the
299
F accumulation increased with the increasing concentration of exogenous F in WT 14
ACS Paragon Plus Environment
Page 14 of 40
Page 15 of 40
Journal of Agricultural and Food Chemistry
300
and transgenic A. thaliana. Interestingly, the F concentration in transgenic A. thaliana
301
was lower than that of the wild type under the same F treatment conditions (Figure
302
8D).
303 304
Subcellular localization of CsFEX in the roots of A. thaliana
305
Subcellular localization prediction software WOLF PSORT28 predicts that
306
CsFEX is localized in the plasma membrane. To further validate the subcellular
307
localization of CsFEX, we constructed a CsFEX:GFP fusion protein and transformed
308
it into A. thaliana. As shown in Figure 9, the GFP signal was distributed in the plasma
309
membrane of A. thaliana root cells (Figure 9A, 9B, 9C), while no fluorescence signal
310
was detected in WT A. thaliana root cells (Figure 9D, 9E, 9F). Therefore, these
311
results are consistent with each other.
312 313
DISCUSSION
314
Recent surveys have indicated that many plants exposed to F often show some
315
morphological symptoms such as chlorosis and tip and leaf edge necrosis
316
suggesting that F is toxic to plants. It is well known that C. sinensis is a crop that
317
hyperaccumulates F, while many studies have shown this F-tolerant plants also
318
exhibit some physiological and biochemical changes in response to high concentration
319
of F, including a decrease of photosynthesis, alteration of leaf antioxidant system, and
320
disruption of the cell ultrastructure
321
concentration of exogenous F induced the new roots to turn black, the young leaves to
44-45.
40-43,
Similarly, this study showed that high
15
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 16 of 40
322
gradually turn yellow, and the edges of the leaves to exhibit scorch symptoms after
323
long-term F treatment (Figure 1A). Additionally, the F content of different tissues in C.
324
sinensis exhibits certain regularity, which mainly appears as mature leaf > young leaf
325
> root/stem 13, 46. As the tissue with the strongest ability to accumulate F in C. sinensis,
326
the leaves are also the strongest tolerant to F. This study revealed that the F content in
327
tea leaves was approximately 43 times that of new roots under normal conditions,
328
indicating that C. sinensis leaves are the main tissue that accumulate F, which is
329
consistent with the previous findings of Gao et al. (2014)
330
Zhang et al. (2013) suggests that F uptake showed biphasic response patterns,
331
following saturable Michaelis-Menten kinetics in the range of low external F, while
332
increased linearly with external supply in the range of high concentrations 47. Here we
333
found that the F content increased significantly with the increase of exogenous F
334
concentration, especially in new roots of C. sinensis, indicating that the new roots can
335
quickly absorb and transfer F
336
clear that although C. sinensis is severely impacted by high concentrations of
337
exogenous F, it is still a hyperaccumulator with higher F-tolerance compared with
338
other species. However, the molecular mechanism driving F tolerance/detoxification
339
in C. sinensis still remains ambiguous.
47.
19.
According to report by
Combining previous reports and our findings, it is
340
The recent discovery of F exporters is a breakthrough in exploring the
341
mechanisms of F resistance; therefore, current research is increasingly focusing on F
342
exporters. Based on reports in prokaryotes and eukaryotes and our previous
343
transcriptome database (PRJNA315669) 33, we identified a fragment that contains two 16
ACS Paragon Plus Environment
Page 17 of 40
Journal of Agricultural and Food Chemistry
344
conserved crcB domains, indicating that this fragment is a typical plant FEX, so we
345
named it CsFEX. Furthermore, the expression of CsFEX in C. sinensis showed
346
tissue-specific and was highest in the young leaves, particularly in the second leaf,
347
and then it was reduced with the increase of leaf maturity. These results indicate that
348
the expression of CsFEX is related to the maturity of C. sinensis leaves which is
349
closely related to the contents of F 48. In the respect of the lower relative expression
350
levels of CsFEX in buds and the first leaf, we speculate that it may be resulted from
351
the fact that the buds and the first leaf have not formed a complete and mature leaf
352
structure compared to the mature leaves. Additionally, the expression of CsFEX in
353
different tissues of C. sinensis can be induced by high concentration of exogenous F
354
treatment in 2 days, indicating that CsFEX respond to exogenous F triggers indeed.
355
To further confirm the functions of CsFEX, prokaryote E. coli was employed to
356
overexpress CsFEX. Our findings indicate that CsFEX recombinant protein confers
357
enhanced F tolerance and lower F content in transformed E. coli cells. Similarly,
358
Baker et al. (2012) reported that the growth of the crcB knockout E. coli strain was
359
significantly inhibited at micromolar concentrations of F with a minimum inhibitory
360
concentration (MIC) slightly higher than 1 mM, while the growth of WT E. coli cells
361
were significantly inhibited at 30 mM NaF, with the MIC of about 200 mM
362
Baker et al. (2012) also suggests that the crcB protein reduces F toxicity by reducing
363
the concentration of F in E. coli cells. Combining published studies with our findings,
364
we therefore speculate that CsFEX can enhance the tolerance to F toxicity in E. coli
365
cells by reducing F accumulation. 17
ACS Paragon Plus Environment
27,
and
Journal of Agricultural and Food Chemistry
366
In the respect to findings of eukaryotes, deletion of the FEX gene in three model
367
eukaryotes (S. cerevisiae, N. crassa, and C. albicans) induces a fluoride-sensitive
368
phenotype, and knock-out cells lacking the FEX gene are 200-1,000 times more
369
sensitive to F than the corresponding WT strain. This directly demonstrates the
370
importance of FEX in resisting F toxicity
371
CsFEX driving F tolerance, model plant A. thaliana was used to construct
372
overexpressing lines in this study. The results of the overexpression study revealed
373
that A. thaliana lines overexpressing CsFEX showed higher germination rates and
374
growth rates with lower F content comparing to the WT under exogenous F treatment.
375
In addition, subcellular localization experiments revealed that the CsFEX is localized
376
in the plasma membrane of A. thaliana root cells, which consists with the results in
377
yeast 30. Therefore, this study demonstrates that overexpression of CsFEX enhances F
378
tolerance in A. thaliana via reducing F content.
28.
To further confirm the mechanism of
379
In summary, this is the first study to identify and clone the F-specific export gene
380
CsFEX from C. sinensis. The expression of CsFEX in C. sinensis is tissue-specific
381
and related to the maturity of leaves; it can be triggered by exogenous F treatment.
382
Furthermore, overexpression of CsFEX in E. coli and A. thaliana confers enhanced
383
tolerance to F toxicity by alleviating F accumulation. These findings directly reveal
384
the effects of CsFEX on alleviating F toxicity. Combing the previous reports and our
385
findings, we speculate that F is passively absorbed by tea plants under high F
386
concentration (Zhang et al., 2013)47 or actively absorbed through some ion channels
387
(such as Ca2+ ATPase) (Li et al., 2017)
25,
and then the putative fluoride export
18
ACS Paragon Plus Environment
Page 18 of 40
Page 19 of 40
Journal of Agricultural and Food Chemistry
388
proteins (CsFEX, CsCLCF) are activated to excrete F from the cytoplasm into the cell
389
wall or apoplast to alleviate F toxicity. On the other way, the excess F can be
390
separated into vacuoles to reduce the toxicity (Figure 10). However, the accurate
391
molecular mechanisms of F accumulation, toxicity/detoxification, and resistance in C.
392
sinensis are warranted more attention to decipher.
393 394
Supporting Information
395
The Supporting Information is available free of charge on the ACS Publications
396
website at xxx.
397
Tertiary structure prediction results of CsFEX protein (Figure S1); RT-PCR
398
identification of CsFEX in transgenic E. coli cells (Figure S2).
399 400
Funding
401
This work was supported by the National Natural Science Foundation of China
402
(31770733), the earmarked fund for China Agriculture Research System (CARS-19)
403
and the earmarked fund for Jiangsu Agricultural Industry Technology System
404
(JATS[2018]280).
405 406
Notes
407
The authors declare no competing interest.
19
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
408
REFERENCES
409
1. Yang, Y.; Liu, Y.; Huang, C. F.; Silva, J. D.; Zhao, F. J. Aluminium alleviates fluoride toxicity in tea
410
( Camellia sinensis ). Plant and Soil. 2016, 402 (1-2), 179-190.
411
2. Cronin, S. J.; Neall, V. E.; Lecointre, J. A.; Hedley, M. J.; Loganathan, P. Research, G., Environmental
412
hazards of fluoride in volcanic ash: a case study from Ruapehu volcano, New Zealand. Journal of
413
Volcanology and Geothermal Research. 2003, 121 (3), 271-291.
414 415
3. Mackowiak, C. L.; Grossl, P. R.; Bugbee, B. G. Biogeochemistry of fluoride in a plant-solution system. Journal of Environment Quality. 2003, 32 (6), 2230-2237.
416
4. Loganathan, P.; Hedley, M. J.; Wallace, G. C.; Roberts, A. H. Fluoride accumulation in pasture
417
forages and soils following long-term applications of phosphorus fertilisers. Environmental
418
Pollution. 2001, 115 (2), 275-282.
419 420
5. Baroni Fornasiero, R. Fluorides effects on hypericum perforatum plants: first field observations. Plant Science. 2003, 165 (3), 507-513.
421
6. Kamaluddin, M.; Zwiazek, J. Fluoride inhibits root water transport and affects leaf expansion and
422
gas exchange in aspen (Populus tremuloides) seedlings. Physiologia Plantarum. 2010, 117 (3),
423
368-375.
424
7. Dey, U.; Mondal, N. K.; Das, K.; Datta, J. K., Dual effects of fluoride and calcium on the uptake of
425
fluoride, growth physiology, pigmentation, and biochemistry of Bengal gram seedlings (Cicer
426
Arietinum L.). Fluoride. 2012, 45 (4), 389-393.
427 428
8. Jha, S. K.; Nayak, A. K.; Sharma, Y. K., Fluoride toxicity effects in onion (Allium cepa L.) grown in contaminated soils. Chemosphere. 2009, 76 (3), 353-356.
20
ACS Paragon Plus Environment
Page 20 of 40
Page 21 of 40
429 430
Journal of Agricultural and Food Chemistry
9. Miller, G. W., The effect of fluoride on higher plants: With special emphasis on early physiological and biochemical disorders. Fluoride. 1993, 26 (1), 3-22.
431
10. Stevens, D. P.; Mclaughlin, M. J.; Alston, A. M. J., Phytotoxicity of the fluoride ion and its uptake
432
from solution culture by Avena sativa and Lycopersicon esculentum. Plant and Soil. 1998, 200 (2),
433
119-129.
434 435
11. Ruan, J.; Ma, L.; Shi, Y.; Han, W. Uptake of fluoride by tea plant (Camellia sinensis L.) and the impact of aluminium. Journal of Science of Food and Agriculture. 2003, 83 (13), 1342–1348.
436
12. Fung, K. F.; Zhang, Z. Q.; Wong, J. W. C.; Wong, M. H. Fluoride contents in tea and soil from tea
437
plantations and the release of fluoride into tea liquor during infusion. Environmental Pollution.
438
1999, 104 (2), 197–205.
439 440
13. Shu, W. S.; Zhang, Z. Q.; Lan, C. Y.; Wong, M. H. Fluoride and aluminium concentrations of tea plants and tea products from Sichuan Province, PR China. Chemosphere. 2003, 52 (9), 1475-1482.
441
14. Weinstein, L. H.; Davison, A. Fluorides in the environment. Fluorides in the Environment. 2004.
442
15. Ruan, J. Y.; Wong, M. H. Accumulation of fluoride and aluminium related to different varieties of
443
tea plant. Environmental Geochemistry and Health. 2001, 23 (1), 53-63.
444
16. Xie, Z.; Chen, Z.; Sun, W.; Guo, X.; Yin, B.; Wang, J. Distribution of aluminum and fluoride in tea
445
plant and soil of tea garden in Central and Southwest China. Chinese Geographical Science. 2007,
446
17 (4), 376-382.
447
17. Liu, Y.; Cao, D.; Ma, L.; Jin, X.; Yang, P.; Ye, F.; Liu, P.; Gong, Z.; Wei, C. TMT-based quantitative
448
proteomics analysis reveals the response of Camellia sinensis to fluoride. Journal of Proteomics.
449
2018, 176 (30), 71-81.
21
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
450 451
18. Gao, H.; Zhu, X.; Panpan, L. I.; Dejiang, N. I.; Chen, Y. Research on adsorption characteristics of tea polysaccharides to fluorine. Journal of Tea Science. 2016, 36 (4): 396-404.
452
19. Gao, H. J. , Zhao, Q. , Zhang, X. C. , Wan, X. C. , Mao, J. D.,, Localization of fluoride and aluminum in
453
subcellular fractions of tea leaves and roots. Journal of Agricultural Food Chemistry. 2014, 62 (10),
454
2313-2319.
455
20. Schneider, T.; Schellenberg, M.; Meyer, S.; Keller, F.; Gehrig, P.; Riedel, K.; Youngsook, L.; Eberl, L.;
456
Martinoia, E. Quantitative detection of changes in the leaf-mesophyll tonoplast proteome in
457
dependency of a cadmium exposure of barley (Hordeum vulgare L.) plants. Proteomics. 2010, 9
458
(10), 2668-2677.
459 460 461 462 463 464
21. Ding, R.; Huang, X. Biogeochemical cycle of aluminium and fluorine in tea garden soil system and its relationship to soil acidification. Acta Pedologica Sinica. 1991, 3. 22. Ruan, J.; Ma, L.; Shi, Y.; Han, W. The impact of pH and calcium on the uptake of fluoride by tea plants (Camellia sinensis L.). Annals of Botany. 2004, 93 (1), 97. 23. Arnesen, A. K. M. Availability of fluoride to plants grown in contaminated soils. Plant and Soil. 1997, 191 (1), 13-25.
465
24. Cai, H. M.; Peng, C. Y.; Chen, J.; Hou, R. Y.; Gao, H. J.; Wan, X. C. X-ray photoelectron spectroscopy
466
surface analysis of fluoride stress in tea (Camellia sinensis (L.) O. Kuntze) leaves. Journal of
467
Fluorine Chemistry. 2014, 158 (158), 11-15.
468
25. Li, Q. S.; Lin, X. M.; Qiao, R. Y.; Zheng, X. Q.; Lu, J. L.; Ye, J. H.; Liang, Y. R. Effect of fluoride
469
treatment on gene expression in tea plant (Camellia sinensis). Scientific Reports. 2017, 7 (1), 9847.
22
ACS Paragon Plus Environment
Page 22 of 40
Page 23 of 40
Journal of Agricultural and Food Chemistry
470
26. Stockbridge, R. B.; Lim, H. H.; Otten, R.; Williams, C.; Shane, T.; Weinberg, Z.; Christopher, M.
471
Fluoride resistance and transport by riboswitch-controlled CLC antiporters. Proceedings of the
472
National Academy of Sciences of the United States of America. 2012, 109 (38), 15289-15294.
473 474 475 476
27. Baker, J. L.; Narasimhan, S.; Zasha, W.; Adam, R.; Stockbridge, R. B.; Breaker, R. R. Widespread genetic switches and toxicity resistance proteins for fluoride. Science. 2012, 335 (6065), 233-235. 28. Stockbridge, R. B.; Robertson, J. L.; Ludmila, K. P.; Christopher, M. A family of fluoride-specific ion channels with dual-topology architecture. eLife. 2013, 2.
477
29. Li, S.; Smith, K. D.; Davis, J. H.; Gordon, P. B.; Breaker, R. R.; Strobel, S. A. Eukaryotic resistance to
478
fluoride toxicity mediated by a widespread family of fluoride export proteins. Proceedings of the
479
National Academy of Sciences. 2013, 110 (47), 19018-19023.
480
30. Smith, K. D.; Gordon, P. B.; Rivetta, A.; Allen, K. E.; Berbasova, T.; Slayman, C.; Strobel, S. A. Yeast
481
Fex1p is a constitutively expressed fluoride channel with functional asymmetry of its two
482
homologous domains. Journal of Biological Chemistry. 2015, 290 (32), 19874.
483 484 485 486
31. Ji, C.; Stockbridge, R. B.; Miller, C. Bacterial fluoride resistance, Fluc channels, and the weak acid accumulation effect. Journal of General Physiology. 2014, 144 (3), 257-261. 32. Last, N. B.; Kolmakova-Partensky, L.; Shane, T.; Miller, C. Mechanistic signs of double-barreled structure in a fluoride ion channel. eLife. 2016, 5.
487
33. Pan, J.; Wang, W.; Li, D.; Shu, Z.; Ye, X.; Chang, P.; Wang, Y. J. B. G. Gene expression profile
488
indicates involvement of NO in Camellia sinensis pollen tube growth at low temperature. BMC
489
Genomics. 2016, 17 (1), 809.
490 491
34. Ghanati, F.; Morita, A.; Yokota, H. Effects of aluminum on the growth of tea plant and activation of antioxidant system. Plant and Soil. 2005, 276 (1-2), 133-141. 23
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
492
35. Wang, Y.; Shu, Z.; Wang, W.; Jiang, X.; Li, D.; Pan, J.; Li, X. CsWRKY2 , a novel WRKY gene from
493
Camellia sinensis, is involved in cold and drought stress responses. Biologia Planterum. 2016, 60
494
(3), 1-9.
495
36. Wang, W.; Wang, Y.; Du, Y.; Zhao, Z.; Zhu, X.; Jiang, X.; Shu, Z.; Yin, Y.; Li, X. Overexpression of
496
Camellia sinensis H1 histone gene confers abiotic stress tolerance in transgenic tobacco. Plant Cell
497
Reports. 2014, 33 (11), 1829-1841.
498 499 500 501
37. Livak, K. J.; Schmittgen, T. D., Analysis of relative gene expression data using real-time quantitative PCR and the 2−ΔΔCT method. Methods. 2001, 25 (4), 402-408. 38. Clough, S. J.; Bent, A. F. Floral dip: a simplified method for Agrobacterium-mediated transformation of Arabidopsis thaliana. Plant Journal. 2010, 16 (6), 735-743.
502
39. Gao H, Zhang Z, Wan X. Influences of charcoal and bamboo charcoal amendment on soil-fluoride
503
fractions and bioaccumulation of fluoride in tea plants. Evironmental Geochemistry and Health.
504
2012, 34 (5), 551-562.
505
40. Fornasiero, R. B. Phytotoxic effects of fluorides. Plant Science. 2001, 161 (5), 979-985.
506
41. Kamaluddin, M.; Zwiazek, J. J. Fluoride inhibits root water transport and affects leaf expansion and
507
gas exchange in aspen (Populus tremuloides) seedlings. Physiologia Plantarum. 2010, 117 (3),
508
368-375.
509 510 511 512
42. Jha, S. K.; Nayak, A. K.; Sharma, Y. K. Fluoride toxicity effects in onion (Allium cepa L.) grown in contaminated soils. Chemosphere. 2009, 76 (3), 353-356. 43. Barbier, O.; Arreola-Mendoza, L.; Razo, L. M. D. Molecular mechanisms of fluoride toxicity. Chemico-Biological Interactions. 2010, 188 (2), 319-333.
24
ACS Paragon Plus Environment
Page 24 of 40
Page 25 of 40
Journal of Agricultural and Food Chemistry
513
44. Cai, H. M.; Dong, Y. Y.; Li, Y. Y.; Li, D. X.; Peng, C. Y.; Zhang, Z. Z.; Wan, X. C. Physiological and
514
cellular responses to fluoride stress in tea (Camellia sinensis) leaves. Acta Physiologiae Plantarum.
515
2016, 38 (6), 144.
516 517
45. Li, C.; Zheng, Y.; Zhou, J.; Xu, J.; Ni, D. Changes of leaf antioxidant system, photosynthesis and ultrastructure in tea plant under the stress of fluorine. Biologia Plantarum. 2011, 55 (3), 563-566.
518
46. Fung, K. F.; Zhang, Z. Q.; Wong, J. W.; Wong, M. H. Aluminium and fluoride concentrations of three
519
tea varieties growing at Lantau Island, Hong Kong. Environmental Geochemistry Health. 2003, 25
520
(2), 219-232.
521 522 523 524
47. Zhang, L.; Li, Q.; Ma, L.; Ruan, J. Characterization of fluoride uptake by roots of tea plants (Camellia sinensis (L.) O. Kuntze). Plant Soil Research. 2013, 366 (1-2), 659-669. 48. Feng, M. L.; Yun, R. J.; Zhi, S. Y. Study on accumulation characteristics of fluorine in tea plants. Acta Agriculturae Zhejiangensis. 2004, 16 (2), 96-98.
25
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
525
Figure legends
526
Figure 1 The effects of F treatment on C. sinensis growth. Changes of young leaves
527
and new roots of C. sinensis treated with different concentrations of F (0 mM control
528
(A, C), 0.84 mM treatment (B, D), respectively) for 20 days. (E) Differences in F
529
content between young leaves and new roots of C. sinensis treated with different
530
concentrations of F for 2 days. Data are presented as mean ± SD. Letters indicate
531
significant differences at P