Subscriber access provided by Service des bibliothèques | Université de Sherbrooke
Characterization of Natural and Affected Environments
Phosphate transporter PvPht1;2 enhances phosphorus accumulation and plant growth without impacting arsenic uptake in plants Yue Cao, Dan Sun, Jun-Xiu Chen, Hanyi Mei, Hao Ai, Guohua Xu, Yanshan Chen, and Lena Q. Ma Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.7b06674 • Publication Date (Web): 14 Mar 2018 Downloaded from http://pubs.acs.org on March 14, 2018
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 21
Environmental Science & Technology
1 2 3
Phosphate transporter PvPht1;2 enhances phosphorus accumulation and plant growth
4
without impacting arsenic uptake in plants
5 6 7
Yue Cao,† Dan Sun,† Jun-Xiu Chen,† Hanyi Mei,† Hao Ai,‡ Guohua Xu,‡ Yanshan Chen*,†
8
Lena Q. Ma†,§
9 10
†State Key Lab of Pollution Control and Resource Reuse, School of the Environment,
11
Nanjing University, Jiangsu 210023, China
12
‡State Key Laboratory of Crop Genetics and Germplasm Enhancement, Key Laboratory of
13
Plant Nutrition and Fertilization in Low-Middle Reaches of the Yangtze River, Ministry of
14
Agriculture, Nanjing Agricultural University, 210095, China
15
§Soil and Water Science Department, University of Florida, Gainesville, FL 32611, United
16
States
17 18 19
*Corresponding author at State Key Laboratory of Pollution Control and Resource Reuse,
20
School of the Environment, Nanjing University, Jiangsu 210023, China; +86 025 8968 0631
21
E-mail addresses:
[email protected],
[email protected] 22 23 24 1
ACS Paragon Plus Environment
Environmental Science & Technology
25
Page 2 of 21
TOC
26 27 28
2
ACS Paragon Plus Environment
Page 3 of 21
Environmental Science & Technology
29
ABSTRACT
30
Phosphorus is an important macronutrient for plant growth and is acquired by plants
31
mainly as phosphate (P). Phosphate transporters (Phts) are responsible for P and arsenate
32
(AsV) uptake in plants including arsenic-hyperaccumulator Pteris vittata. P. vittata is
33
efficient in AsV uptake and P utilization, but the molecular mechanism of its P uptake is
34
largely unknown. In this study, a P. vittata Pht, PvPht1;2, was cloned and transformed into
35
tobacco (Nicotiana tabacum). In hydroponic experiments, all transgenic lines displayed
36
markedly higher P content and better growth than wild type, suggesting that PvPht1;2
37
mediated P uptake in plants. In addition, expressing PvPht1;2 also increased the shoot/root
38
32
39
mediated P translocation in plants. Unlike many Phts permeable to AsV, PvPht1;2 showed
40
little ability to transport AsV. In soil experiments, PvPht1;2 also significantly increased shoot
41
biomass without elevating As accumulation in PvPht1;2 transgenic tobacco. Taken together,
42
our results demonstrated that PvPht1;2 is a specific P transporter responsible for P acquisition
43
and translocation in plants. We envisioned that PvPht1;2 can enhance crop P acquisition
44
without impacting AsV uptake, thereby increasing crop production without compromising
45
food safety.
P ratio by 69–92% and enhanced xylem sap P by 46–62%, indicating that PvPht1;2 also
46
3
ACS Paragon Plus Environment
Environmental Science & Technology
47 48
Page 4 of 21
INTRODUCTION
Phosphorus is a major essential macronutrient for plant growth, which is involved in
49
many metabolic pathways. Plants take up phosphorus exclusively in the form of inorganic
50
phosphate (P). Because of its high fixation in soils and slow diffusion to the root surface,
51
plants have evolved strategies to increase the availability of soil P.1 In plants, the high-affinity
52
P transporters (Phts/PTs) play key roles in P acquisition from soil.2 These P transporters are
53
categorized into four subfamilies: Pht1, Pht2, Pht3, and Pht4.3 Over the past decades, many
54
genes that encode PTs have been identified and cloned from A. thaliana and cereal, legume,
55
and solanaceous species.4-11
56
In Arabidopsis, Pht1 subfamily is comprised of 9 members (AtPht1;1 to 1;9). Among
57
them, AtPht1;1 and AtPht1;4 are responsible for P acquisition under both high- and low-P
58
conditions.12, 13 The P uptake by atpht1;1/atpht1;4 double mutant was 75% lower than wild
59
type (WT) plants.13 In addition, as high-affinity P transporters, AtPht1;8 and AtPht1;9 play
60
key roles in P uptake under P-deficient conditions.10
61
In rice (Oryza sativa), 13 Pht1 genes are known in the genome.4 Among them, OsPht1;1,
62
1;2, 1;4, 1;6, 1;8, 1;9 and 1;10 mediate P uptake and translocation in rice.14, 15 OsPT1 is
63
constitutively expressed in plants, functioning in P uptake and translocation under
64
P-sufficient conditions.9 Similarly, OsPht1;8 is expressed in various tissues under both
65
P-sufficient and -deficient conditions, and is up-regulated in the roots under P-deficient
66
conditions.7 OsPht1;6 is mainly expressed in the roots, involving in P uptake under
67
P-deficient conditions.6 Recently, the function of OsPht1;4 has been characterized, which
68
facilitates P acquisition and mobilization in rice.11
69
Arsenic (As) and P are chemical analogs. However, As is a toxic element and ubiquitous
70
in soils, which can be taken up by crops, thereby threatening human health through food
71
chain.16, 17 Due to their similarity, AsV can be taken up and translocated via PTs.13, 18, 19 In
72
Arabidopsis, AsV is taken up via AtPht1;1 and AtPht1;4.13, 20 In rice, OsPht1;1, Os Pht1;4 and
73
OsPht1;8 are involved in AsV uptake and translocation, and their modulation affects As
4
ACS Paragon Plus Environment
Page 5 of 21
Environmental Science & Technology
74
accumulation in rice.19, 21, 22 Though overexpression of PTs promotes P acquisition,14 it may
75
also increase As uptake by plants.21, 23
76
Chinese brake fern (Pteris vittata) is the first-known As-hyperaccumulator, it is efficient
77
in As uptake, translocation and detoxification.24, 25 Besides, the fern is also efficient in
78
acquiring P from insoluble P sources in soils,26, 27 and efficient in depleting P from
79
hydroponic solution.28 Recently, P. vittata P transporters PvPht1;1 to PvPht1;3 have been
80
characterized.29 Yeast experiments showed that PvPht1;3 is a high-affinity AsV transporter.29
81
However, the functions of PvPht1;1 and PvPht1;2 in plants have not been elucidated, so their
82
role in improving P utilization is unclear.
83
PvPht1;1 and PvPht1;2 encode predicted proteins of 536 amino acids, which share 98.5%
84
identity.29 With only few nucleotides being different, they can be considered as the same gene.
85
In this work, to study the function of PvPht1;2 and its role in P uptake in plants, we
86
transformed PvPht1;2 into model plant tobacco and investigated its function in P and AsV
87
uptake and translocation by transgenic tobacco. We believe that this study may provide
88
important insights into the behavior of PvPht1;2 as well as provide a potential strategy to
89
enhance crop P acquisition.
90
MATERIALS AND METHODS
91
Growth of P. vittata. Spores of P. vittata were collected from Florida, USA24 and
92
preserved in our lab at Nanjing University. Their spores were sown on potting soils, watered
93
and covered with transparent plastic films to keep the soil moist. After 2 months of
94
cultivation, sporophyte seedlings with 2–3 fronds appeared, which were then transplanted
95
into separate pots following Fu et al.28 All sporophytes were cultivated in a greenhouse to
96
4-frond stage and then acclimated in 500 mL aerated 0.2 strength (0.2X) Hoagland nutrient
97
solution (HNS) for 7 d.28 For the transcripts analysis, sporophyte seedlings were transferred
98
0.2X HNS containing 100 µM KH2PO4 (+P) , 0 µM KH2PO4 (–P) or 100 µM KH2PO4/50 µM
99
Na2HAsO4·7H2O (+As) for 3 days. All ferns were grown under a 14 h photoperiod, 26/20◦C
100
day/night temperature, 60% relative humidity, and 3000 lux light intensity.
5
ACS Paragon Plus Environment
Environmental Science & Technology
101
Total RNA Preparation and qRT-PCR analysis in P. vittata. Total RNAs from P.
102
vittata roots and fronds were isolated using Plant Total RNA Kit (Sigma-Aldrich), reverse
103
transcription and first-strand cDNA was synthesized using HiScript II One Step RT-PCR Kit
104
(Vazyme Biotech, Nanjing, China). qRT-PCR analysis was performed using SYBR Green
105
PCR Master Mix (Vazyme Biotech, Nanjing, China), and the CFX Connect Real-Time PCR
106
Detection System (BIO-RAD). Relative expression levels of PvPht1;2 (Accession No.
107
KM192136) were computed by 2-∆∆CT method of relative quantification. P. vittata Actin gene
108
(PvActin) and Histone gene (PvHistone)30 were used as an internal control. All gene-specific
109
primers used for qRT-PCR are as follows. PvPHT1;2: 5'-GCC CTG GTA TTG GCC ACA
110
AG-3' and 5'-CCT CGA GGG AGC GAC CAT TT-3'; PvActin: 5'-GGG CAG TAT TTC
111
CAA GCA TAG TGG G-3' and 5'-TGC CTC GCT TTG ATT GAG CCT CAT C-3';
112
PvHistone: 5'-GGG TTT ACA TTC AGC GAA GC-3' and 5'-GCT TTC CCT CCA GTG
113
GAC TT-3'.
114
Page 6 of 21
Yeast Vector Construction, Yeast Transformation and Growth Assays. PvPht1;2
115
coding sequence was cloned from cDNA of P. vittata collected from Florida, USA using the
116
following primers: 5’-ATG GCA AAA CTA GAG GTC CTC ACC G-3’ and 5’-CTA TGA
117
TGT GTG TGT AGC ACC CCC A-3’. Adapters were added to PvPht1;2 CDS using the
118
following primers: 5’-gaa aaa acc ccg gat tct aga ATG GCA AAA CTA GAG GTC CTC
119
ACC G-3’ and 5’-taa cta att aca tga ctc gag CTA TGA TGT GTG TGT AGC ACC CCC A-3’
120
(underlining indicates recombination sequences). The PCR product was then cloned into the
121
GAL1 promoter cassette of pAG413GAL-ccdB (Addgene, http://www.addgene.org/) between
122
XbaI and XhoI restriction sites by recombination, using the Trelief™ SoSoo Cloning Kit
123
(TSING KE, Nanjing, China). The yeast (Saccharomyces cerevisiae) strain for heterologous
124
expression of PvPht1;2 was the ∆pho84 mutant (Thermo Scientific,
125
https://www.openbiosystems.com) with the BY4741 (MATa his3∆1 leu2∆0 met15∆0 ura3∆0)
126
background.31, 32 The methods related to yeast transformations mainly referred to the high
127
efficiency transformation of yeast described by Gietz et al.33
128
Yeast growth assay was performed according to Chen et al5. Briefly, yeast cells were 6
ACS Paragon Plus Environment
Page 7 of 21
Environmental Science & Technology
129
grown at 30°C in synthetic defined (SD) medium (0.67% yeast nitrogen base) without amino
130
acids, containing 2% (w/v) glucose or 2% (w/v) galactose (induction medium), supplemented
131
with yeast synthetic dropout without histidine at pH 5.8. For AsV tolerance assays, yeast was
132
grown in liquid SD medium (with 2% [w/v] glucose) to an OD600 of ~1.0 and then subjected
133
to centrifugation and dilution with sterile water. The drop assays were performed on SD
134
plates (with 2% [w/v] galactose) containing 1.0 mM AsV for ∆pho84 expressing PvPht1;2.
135
Plant expression vector construction and transgenic plant generation and selection.
136
Adapters were added to PvPht1;2 CDS using the following primers:5’-acg ggg gac tct aga
137
gga tcc ATG GCA AAA CTA GAG GTC CTC ACC G-3’ and 5’-ggg aaa ttc gag ctc ggt acc
138
CTA TGA TGT GTG TGT AGC ACC CCC A-3’ (underlining indicates recombination
139
sequences). The PCR product was then cloned into the 35S promoter cassette of pSN1301
140
(pCAMBIA1301, CAMBIA) between BamHI and KpnI restriction sites by recombination,
141
using the CloneEZ PCR Cloning Kit (Genscript, Nanjing, China), with the constructed binary
142
vector being named pSN1301-PvPT1;2. Agrobacterium strain C58 was transformed with the
143
binary vector pSN1301-PvPT1;2 by electroporation. Transformation of tobacco leaf explants
144
was carried out following Curtis et al. and Gallois & Marinho et al.34, 35 Transgenic plants
145
were then identified via hygromycin resistance and GUS staining.
146
Semi-quantitative RT-PCR analysis of transgenic tobaccos. Total RNA was
147
extracted from tobacco seedlings. The first-strand cDNA was synthesized from 2 µL total
148
RNA using HiScript II One Step RT-PCR Kit (Vazyme Biotech, Nanjing, China), which was
149
used as RT-PCR templates. The cDNAs of PvPht1;2 were amplified by PCR for 30 cycles
150
using the gene-specific primers 5'-GCC CTG GTA TTG GCC ACA AG-3' and 5'-CCT CGA
151
GGG AGC GAC CAT TT-3'. Tobacco actin was amplified for 30 cycles as an expression
152
control using the LeActin primer 5'-TTC CGT TGC CCA GAG GTC CT-3' and 5'-GGG
153
AGC CAA GGC AGT GAT TTC-3'.
154
Growth of transgenic tobacco in different P and As conditions. In hydroponic
155
experiments, transgenic tobacco seeds and wild type (WT) seeds were germinated in 1/5 MS
156
media. Uniform 2-week old tobacco seedlings were transferred to 0.2X HNS containing 100 7
ACS Paragon Plus Environment
Environmental Science & Technology
Page 8 of 21
157
µM KH2PO4 (+P) or 10 µM KH2PO4 (–P) for 14 d. For As accumulation determination,
158
seedlings were exposed to 20 µM AsV (Na2HAsO4·7H2O, Sigmae-Aldrich, USA) for 3 days.
159
For inorganic P determination, PvPht1;2–Ox lines and WT plants were cultured in 0.2X HNS
160
for 14 d under P-deficient condition, and then transferred to P-sufficient (100 µM) solution
161
for 7 d. In soil test, transgenic and WT tobacco seeds were germinated and cultivated in a
162
garden soil. In addition, uniform 7-d old tobacco seedlings were transferred into soils
163
containing 0, 10, 20, and 40 mg kg–1 AsV for 30 d. 32
164
P uptake assay and xylem sap collection in tobacco. After growing in 0.2X HNS for
165
7 d, tobaccos were transferred into 0.2X HNS (200 mL) labeled with 8 µCi of 32P (KH2PO4,
166
Perkin-Elmer, Waltham, MA, USA) and cultivated for 12 h. Then the plant roots were
167
incubated in ice-cold desorption solution (0.5 mM CaCl2, 100 µM NaH2PO4, 2 mM MES, pH
168
5.5) for 10 min to remove 32P. The plants were then blotted-dry, the roots and shoots were
169
harvested, and their fresh weights were measured. Tissues were digested in HClO4 and 30%
170
(v/v) H2O2 mixture at 70°C for 2–3 h. Scintillation cocktail (3 mL) was added to the digested
171
tissue and liquid scintillation counter (Tri–Carb 2100, Packard) was employed to determine
172
32
173
P activity. Transgenic and WT tobacco seedlings were cultured under 0.2X HNS. Briefly, the stems
174
of tobacco were cut at 2 cm above the roots. The cut surfaces were rinsed with deionized
175
water and blotted dry. The xylem sap was collected by pipette from the cut surface for 2 h.
176
The inorganic P concentration of xylem sap was determined as described below.
177
P and As determination in plants. Total P concentrations of plant samples were
178
measured according to Chen et al.5 Briefly, ~0.05 g of crushed dry samples were digested
179
with H2SO4–H2O2 at 280℃. After cooling, the digested samples were diluted to 100 mL in
180
distilled water. P concentration was analyzed by the molybdenum blue method based on dry
181
weight.36
182
For inorganic P in plant, ~ 0.5 g fresh samples were used.36 Briefly, the samples were
183
homogenized in 1 mL of 10% (w/v) perchloric acid using an ice-cold mortar and pestle. The
184
homogenate was then diluted 10 times with 5% (w/v) perchloric acid and placed on ice for 30 8
ACS Paragon Plus Environment
Page 9 of 21
Environmental Science & Technology
185
min. After centrifugation at 10,000 g for 10 min at 4℃, the supernatant was used for P
186
measurement via the molybdenum blue method. The absorption values for the solution at 820
187
nm were determined using a spectrophotometer (SHIMADZUUV-2550).
188
For As analysis, fresh plants were separated into the shoots and roots, lyophilized
189
(FreezZone 12, LABCONCO) and stored at -80℃. For total As, freeze-dried plant sample
190
(0.05 g ) was digested with 50% HNO3 at 105℃ following USEPA Method 3050B and
191
determined by inductively coupled plasma mass spectrometry (ICP-MS; PerkinElmer
192
NexION 300X, USA; detection limit at 0.1 µg L-1).
193
QA/QC and statistical analysis. For quality assurance and quality control (QA/QC),
194
indium was used as internal standards and was added into the samples, calibration standards,
195
and blanks. During measurement, standard solution at 5 µg L-1 As was measured every 20
196
samples to monitor the stability of ICP-MS. The check recovery was within 90–110%. In
197
addition, blanks and certified reference material for plant samples (GSB 21, Chinese
198
geological reference materials) were included for quality assurance, which were within
199
expected values.37
200
Data are presented as the mean of 3–5 replicates with standard error. Analysis of
201
variance (ANOVA) was carried out by SPSS software (SPSS 13.0; SPSS Inc, Chicago, USA).
202
Significant differences were determined with treatment means compared by Tukey’s mean
203
grouping tests at p < 0.05.
204
RESULTS AND DISCUSSION
205
Identification and Expression pattern of P. vittata P Transporter PvPht1;2
206
To understand the molecular mechanism of P metabolism in P. vittata, 6 putative Pht
207
sequences were identified, including PvPht1;2. Then transcriptional expression of PvPht1;2
208
in P. vittata was investigated by qRT-PCR using actin and histone as reference genes. As
209
shown in Figure 1A, PvPht1;2 was expressed strongly in the roots and fronds, with frond
210
transcripts level of PvPht1;2 being 42% higher than root.
211 212
It is known that P deficiency induces Pht expression in plants. Besides, as an analog, AsV is also taken up by Pht transporters in plants, so it may affect Pht transcription in plants. 9
ACS Paragon Plus Environment
Environmental Science & Technology
Page 10 of 21
213
Thus, we investigated the expression of PvPht1;2 responding to P deficiency (no P) or AsV
214
exposure (50 µM AsV). In the roots, the expression of PvPht1;2 was 8.5-fold higher under
215
P-deficient condition than that under P-sufficient condition (Figure 1B). When P. vittata was
216
exposed to AsV, transcripts level of PvPht1;2 in the roots was comparable to no As control
217
(Figure 1B).The results were similar to P. vittata’s expression pattern in DiTusa et al.29 In the
218
fronds, the expression of PvPht1;2 transcripts was similar in different treatments (Figure 1C).
219
These results showed that PvPht1;2 transcripts were induced by P deficiency in P. vittata
220
roots, but not by AsV, indicating that PvPht1;2 may play a critical role in P acquisition but
221
not As uptake in P. vittata.
222
Overexpression of PvPht1;2 increased P uptake and translocation in tobacco plants
223
To characterize its function in P uptake and translocation in plants, we generated
224
PvPht1;2 transgenic tobacco lines (PvPht1;2-Ox), where PvPht1;2 was expressed under
225
constitutive CaMV35S promoter. Three independent transgenic T2 lines (Ox1, Ox10, and
226
Ox21) were selected to assess its effects on P acquisition (Figure 2). RT-PCR analysis showed
227
that PvPht1;2 transcripts were strongly expressed in PvPht1;2–Ox lines, while it was not
228
detected in WT plants (Figure 2C).
229
In hydroponic experiments, PvPht1;2-Ox lines and WT plants were cultured under
230
P-sufficient and -deficient conditions for 14 d (Figure 2). All three transgenic plants grew
231
similarly as WT under P-sufficient treatment (Figure 2AD). However, Ox1, Ox10, and Ox21
232
displayed better growth than WT under P-deficient condition, with 26, 50, and 67% higher
233
root biomass and 34, 64, and 66% higher shoot biomass, respectively (Figure 2BE). The
234
results indicated that PvPht1;2 may play a crucial role in enhancing P acquisition in
235
transgenic tobaccos, thereby promoting plant growth at P-deficient condition.
236
To test this hypothesis, we measured P concentrations in PvPht1;2-Ox lines. Under
237
P-sufficient condition, P concentrations of Ox1, Ox10, and Ox21 shoots were 21, 29, and 28%
238
higher in the roots, and 17, 14, and 17% higher in the shoots than that of WT, respectively
239
(Figure 2F), indicating that expressing PvPht1;2 promoted P acquisition by plants. Under
240
P-deficient conditions, expressing PvPht1;2 enhanced Ox1, Ox10, and Ox21 root P 10
ACS Paragon Plus Environment
Page 11 of 21
Environmental Science & Technology
241
concentrations by 13, 22, and 21%, respectively (Figure 2G). In contrast, total P
242
concentration in the shoots of transgenic lines showed no significant difference with that in
243
WT (Figure 2G). However, considering the increased biomass of Ox1, Ox10 and Ox21
244
(Figure 2E), we concluded that heterologous expression of PvPht1;2 increased P acquisition
245
by plants, thereby promoting plant growth under P-deficient condition.
246
To further understand the underlying mechanism, 32P radioisotope assay was employed.
247
After cultivating in 0.2X HNS for 14 d, seedlings of PvPht1;2 transgenic lines and WT were
248
incubated in 0.2X HNS containing 8 µCi of 32P for 12 h. The results showed that 32P uptake
249
rates of transgenic lines reached 0.25–0.30 nmol mg-1 root FW, 31–57% higher than that of
250
WT, further proving that expressing PvPht1;2 increased P uptake by transgenic plants (Figure
251
3A).
252
After plant uptake, P is loaded from root cortical cells into the xylem and translocated to
253
the shoots, which is also mediated by P transporters.38 To further investigate whether
254
PvPht1;2 also mediated P translocation, 32P translocation factors (shoot/ root 32P) were
255
analyzed. The results showed that 32P translocation factors of PvPht1;2-Ox lines were 0.99–
256
1.1, being 69–92% higher than that of WT (Figure 3B), indicating that PvPht1;2 also
257
facilitated P translocation in transgenic plants. P concentration in the xylem sap is an
258
important factor to characterize P translocation from the roots to shoots. The P concentration
259
in the xylem sap of PvPht1;2 transgenic lines were 46–62% higher than that of WT (Figure
260
3C), which was consistent with the increased translocation factors, further proving that
261
PvPht1;2 mediated P translocation in transgenic plants.
262
Besides total P in plant tissues, we also determined the inorganic P concentration in
263
PvPht1;2-Ox lines. As a main species in plants, inorganic P concentration can be used to
264
indicate their P nutrition. After cultured in 0.2X HNS for 14 d under P-deficient condition,
265
PvPht1;2–Ox lines and WT plants grown in P-sufficient (100 µM) solution for 7 d.
266
Compared with WT plants, the root inorganic P concentration of PvPht1;2-Ox lines showed
267
no significant difference, but shoot concentrations in Ox1, Ox10, and Ox21 lines were 42, 39,
11
ACS Paragon Plus Environment
Environmental Science & Technology
268
and 50% higher (Figure 3D), further confirming the critical role of PvPht1;2 in plant P
269
translocation.
270
Page 12 of 21
In plants, P uptake and translocation are mediated by Phts.2 So, increasing number of
271
Phts have been identified and functionally characterized, with the Pht1 subfamily being
272
widely studied.39 In this study, overexpression PvPht1;2 resulted in higher P uptake, and root
273
to shoot translocation factor (Figure 3AB), and increased P accumulation under P-deficient
274
and -sufficient conditions (Figure 2). The results suggested that PvPht1;2 may play an
275
important role in P uptake, and root to frond transport in P. vittata. Considering its high
276
expression level in the fronds (Figure 1A), PvPht1;2 might also be involved in frond P
277
mobilization.
278
PvPht1;2 showed low arsenate transport capacity in hydroponic solution
279
Due to their chemical similarity, P transporters not only transport P but also AsV. To test
280
whether PvPht1;2 mediated AsV transport, we examined the growth of ∆pho84 yeast cells
281
expressing PvPht1;2 in the presence of AsV. Compared with empty vector control, ∆pho84
282
expressing PvPht1;2 showed little differences when grown on the SD medium containing
283
AsV (Figure 4A). Due to the deletion of yeast P/AsV transporter Pho84, ∆pho84 transformed
284
with empty vector accumulated less As than its wild type BY4741 (Figure 4B). Moreover, As
285
accumulation in ∆pho84 expressing PvPht1;2 was comparable to that with empty vector
286
(Figure 4B), suggesting that PvPht1;2 was incapable of complementing pho84 deletion. This
287
was different from P transporter PvPht1;3, which showed high affinity for AsV when
288
expressed in yeast and may play a critical role in efficient AsV uptake in P. vittata.29 These
289
results indicated that PvPht1;2 was not permeable to AsV, thus conferring little impact on
290
AsV accumulation in yeast.
291
Because PvPht1;2 increased plant P uptake and promoted plant growth, PvPht1;2 gene
292
can be used to enhance P acquisition by food crops to decrease consumption of P fertilizer
293
and increase crop production. However, considering As is ubiquitous in soils and many P
294
transporters also facilitate AsV uptake in plants, it is important to consider As uptake by
295
PvPht1;2. Thus, PvPht1;2-Ox lines were exposed to 20 µM AsV hydroponically for 3 d and 12
ACS Paragon Plus Environment
Page 13 of 21
Environmental Science & Technology
296
As accumulation in tobacco were determined. The As concentration in PvPht1;2-Ox lines and
297
WT plants were comparable (Figure 4CD). Overexpression PvPht1;2 did not cause As
298
accumulation in transgenic plants, suggesting that PvPht1;2 may contribute little to As uptake
299
or translocation in P. vittata.
300
Taken together, our results showed that PvPht1;2 was an efficient P transporter but
301
didn’t mediate AsV uptake by plants, which is different from known P transporters. For
302
example, OsPht1;1 and OsPht1;8 play key roles in P absorption, so they have been used to
303
improve P acquisition by plants via transgenic approach.9 However, while both OsPht1;1 and
304
OsPht1;8 increase P uptake in transgenic plants, they also enhance As accumulation in
305
plants.21, 23 For example, in hydroponic solution, overexpression of OsPht1;1 enhanced As
306
accumulation in rice by 41-47%.21 Moreover, OsPht1;8 overexpression lines accumulated
307
4.6-5.6 folds higher As.23 Different from OsPht1;1 and OsPht1;8, however, PvPht1;2
308
overexpression lines showed strong transport ability for P without impacting As accumulation
309
under different P regimes. Thus, it could be used as a candidate gene to improve P absorption
310
and utilization efficiency in crops.
311
Expression of PvPht1;2 promoted plant growth without impacting As uptake by tobacco
312
in soil experiment
313
Under hydroponic condition, P was supplied as KH2PO4, which is soluble and available
314
for plant uptake. In contrast, in soil, P is often sorbed by Fe/Al oxides, resulting in low
315
availability.14 Since PvPht1;2 overexpression increased P uptake and translocation without
316
impacting As accumulation in plants under hydroponic cultivation, it is important to validate
317
its effects on plant growth and As accumulation in soils.
318
Therefore, we grew tobaccos for 30 d in a soil, which contained 8.11 mg kg–1 soluble P
319
and was spiked with 0, 10, 20, and 40 mg kg–1 AsV. Compared with WT, shoot biomass of
320
PvPht1;2-Ox lines was 54–92, 51–108, 122–285 and 9.1–27% higher in 4 treatments (Figure
321
4E). With comparable P concentrations and higher biomass (data not shown), total P content
322
of PvPht1;2–Ox lines were higher than that of WT, consistent with hydroponic experiments.
323
Based on their function characterization, expressing P transporters is a promising 13
ACS Paragon Plus Environment
Environmental Science & Technology
Page 14 of 21
324
approach to engineer low-P tolerance in transgenic plants.38 Expressing HvPht1;1/6,40
325
OsPht1;19 and AtPht1;58 improved P acquisition and utilization efficiency in barley, rice and
326
Arabidopsis. However, overexpression of a P transporter does not guarantee better growth.
327
For example, overexpression of OsPht1;8 and OsPht1;2 causes P toxicity.6, 7 On the other
328
hand, many P transporters have affinity for AsV, with only limited P transporters being
329
characterized for AsV transport. Though they can increase P concentration in plants, they
330
may also increase plant As uptake, causing food safety issue. However, in our study, even in
331
As-contaminated soils, expression of PvPht1;2 didn’t increase As concentrations in plant
332
shoots (Figure 4F), which is of significance for food safety.
333
In summary, this study showed that the P. vittata P transporter, PvPht1;2, is efficient in P
334
uptake and translocation in transgenic tobaccos. Hence, expressing PvPht1;2 increased P
335
content and promoted plant growth in tobacco plants in hydroponic and soil experiments.
336
While many Phts are permeable to AsV, PvPht1;2 showed little capacity to transport AsV,
337
therefore expressing PvPht1;2 didn’t increase As uptake in plants. Based on the results, we
338
envisioned that PvPht1;2 transgenic approach can be used to enhance crop P acquisition
339
without increasing As uptake, thereby improving crop production and food safety.
340 341
ACKNOWLEDGEMENTS
342
This work was supported by the National Natural Science Foundation of China (Grant No.
343
21637002 and 21707068), Jiangsu Provincial Natural Science Foundation of China (No.
344
BK20160649) and the National Key Research and development program of China (Grant No.
345
2016YFD0800801).
346
14
ACS Paragon Plus Environment
Page 15 of 21
Environmental Science & Technology
347 348
Figure 1. Transcriptional patterns of PvPht1;2 in P. vittata sporophytes growing in 0.2X
349
Hoagland nutrient solution (HNS) (A), and transcriptional levels of PvPht1;2 in the roots (B)
350
and fronds (C) responding to P-deficiency or As exposure. P. vittata were grown in 0.2X
351
HNS containing 100 µM P (+P), 0 µM P (–P) or 100 µM P/50 µM As (+As) for 21 d. Error
352
bars indicate SE of three biological replicates.
353
15
ACS Paragon Plus Environment
Environmental Science & Technology
Page 16 of 21
354 355
Figure 2. Growth performances of PvPht1;2 overexpressing lines (Ox1; 10; and 21) and WT
356
plants under different P levels. 14-d old transgenic and WT plants were grown in 0.2X HNS
357
containing 100 µM P (+P) or 10 µM P (–P) for 14 d. Phenotype of PvPht1;2 overexpressing
358
lines compared with WT under +P (A) or –P (B) solution; Relative expression of PvPht1;2 in
359
transgenic lines and WT plants by semi-RT PCR (C); Biomass (DE) and total P
360
concentration (FG) of PvPht1;2 overexpressing lines and WT under +P (DF) or –P (EG)
361
conditions. Error bars represent SE (n=5). Means marked with different letters indicate
362
significant differences (p < 0.05). FW, fresh weight.
363 364
16
ACS Paragon Plus Environment
Page 17 of 21
Environmental Science & Technology
365 366
Figure 3. Uptake rate and root to shoot translocation of 32P and P concentration in xylem sap,
367
roots and shoots of PvPht1;2-Ox lines and WT plants. A, 32P uptake rate of PvPht1;2-Ox
368
lines and WT; B, shoot-to-root ratios of the 32P taken up by PvPht1;2-Ox lines and WT; C, P
369
concentration in xylem sap of PvPht1;2-Ox lines and WT; and D, inorganic P concentration
370
in PvPht1;2-Ox lines under P re-supply condition. After grown in 0.2X HNS lacking of P for
371
14 d, plants were transferred to P–sufficient (100 µM) solution 7 d. Error bars represent SE
372
and n=3 for AB and n=5 for CD. Means marked with different letters indicate significant
373
differences (p < 0.05). FW, fresh weight.
374 375
17
ACS Paragon Plus Environment
Environmental Science & Technology
Page 18 of 21
376 377
Figure 4. Arsenic concentrations in yeast and plants expressing PvPht1;2. Phenotype (A) and
378
As concentration (B) of yeast mutant ∆pho84 transformed with vector or vector containing
379
PvPht1;2. Arsenic concentrations in the roots (C) and shoots (D) of PvPht1;2 overexpression
380
lines and WT plants under P -sufficient (+P) and -deficient (–P) conditions, and plant growth
381
(E) and As concentration (F) of PvPht1;2-Ox lines and WT plants after growing for 21 d in
382
soil containing 0, 5, 10, or 20 mg kg–1 of As, and Error bars represent SE (n=5) and means
383
marked with different letters indicate significant differences (p < 0.05). DW, dry weight.
384 385 386 387
18
ACS Paragon Plus Environment
Page 19 of 21
Environmental Science & Technology
388
References
389
(1) Wu, P.; Shou, H.; Xu, G.; Lian, X. Improvement of phosphorus efficiency in rice on the basis of
390
understanding phosphate signaling and homeostasis. Curr. Opin. Plant Biol. 2013, 16, 205-212.
391
(2) Raghothama, K. G. Phosphate acquisition. Annu. Rev. Plant Physiol. Plant Mol. Biol. 1999, 50, 665-693.
392
(3) Liu, F.; Chang, X. J.; Ye, Y.; Xie, W. B.; Wu, P.; Lian, X. M. Comprehensive sequence and whole-life-cycle
393
expression profile analysis of the phosphate transporter gene family in rice. Mol. Plant 2011, 4, 1105-1122.
394
(4) Paszkowski, U.; Kroken, S.; Roux, C.; Briggs, S. P. Rice phosphate transporters include an evolutionarily
395
divergent gene specifically activated in arbuscular mycorrhizal symbiosis. Proc. Natl. Acad. Sci. U.S.A. 2002, 99,
396
13324-13329.
397
(5) Chen, A.; Hu, J.; Sun, S.; Xu, G. Conservation and divergence of both phosphate- and mycorrhiza-regulated
398
physiological responses and expression patterns of phosphate transporters in solanaceous species. New phytol.
399
2007, 173, 817-831.
400
(6) Ai, P.; Sun, S.; Zhao, J.; Fan, X.; Xin, W.; Guo, Q.; Yu, L.; Shen, Q.; Wu, P.; Miller, A. J.; Xu, G. Two rice
401
phosphate transporters, OsPht1;2 and OsPht1;6, have different functions and kinetic properties in uptake and
402
translocation. Plant J. 2009, 57, 798-809.
403
(7) Jia, H.; Ren, H.; Gu, M.; Zhao, J.; Sun, S.; Zhang, X.; Chen, J.; Wu, P.; Xu, G. The phosphate transporter
404
gene OsPht1;8 is involved in phosphate homeostasis in rice. Plant Physiol. 2011, 156, 1164-1175.
405
(8) Nagarajan, V. K.; Jain, A.; Poling, M. D.; Lewis, A. J.; Raghothama, K. G.; Smith, A. P. Arabidopsis Pht1;5
406
mobilizes phosphate between source and sink organs and influences the interaction between phosphate
407
homeostasis and ethylene signaling. Plant Physiol. 2011, 156, 1149-1163.
408
(9) Sun, S.; Gu, M.; Cao, Y.; Huang, X.; Zhang, X.; Ai, P.; Zhao, J.; Fan, X.; Xu, G. A constitutive expressed
409
phosphate transporter, OsPht1;1, modulates phosphate uptake and translocation in phosphate-replete rice. Plant
410
Physiol. 2012, 159, 1571-1581.
411
(10) Remy, E.; Cabrito, T. R.; Batista, R. A.; Teixeira, M. C.; Sa-Correia, I.; Duque, P. The Pht1;9 and Pht1;8
412
transporters mediate inorganic phosphate acquisition by the Arabidopsis thaliana root during phosphorus
413
starvation. New Phytol. 2012, 195, 356-371.
414
(11) Zhang, F.; Sun, Y.; Pei, W.; Jain, A.; Sun, R.; Cao, Y.; Wu, X.; Jiang, T.; Zhang, L.; Fan, X.; Chen, A.; Sun,
415
S.; Xu, G. Involvement of OsPht1;4 in phosphate acquisition, and mobilization facilitates embryo development
416
in rice. Plant J. 2015, 82, 556-569.
417
(12) Misson, J.; Thibaud, M. C.; Bechtold, N.; Raghothama, K.; Nussaume, L. Transcriptional regulation and
418
functional properties of Arabidopsis Pht1;4, a high affinity transporter contributing greatly to phosphate uptake
419
in phosphate deprived plants. Plant Mol. Biol. 2004, 55, 727-741.
420
(13) Shin, H.; Shin, H. S.; Dewbre, G. R.; Harrison, M. J. Phosphate transport in Arabidopsis: Pht1;1 and Pht1;4
421
play a major role in phosphate acquisition from both low- and high-phosphate environments. Plant J. 2004, 39,
422
629-642.
423
(14) Gu, M.; Chen, A.; Sun, S.; Xu, G. Complex regulation of plant phosphate transporters and the gap between
424
molecular mechanisms and practical application: What is missing? Mol. Plant 2016, 9, 396-416.
425
(15) Wang, D.; Lv, S.; Jiang, P.; Li, Y. Roles, regulation, and agricultural application of plant phosphate
426
transporters. Front. Plant Sci. 2017, 8, 817.
427
(16) Li, G.; Sun, G. X.; Williams, P. N.; Nunes, L.; Zhu, Y. G. Inorganic arsenic in Chinese food and its cancer
428
risk. Environ. Int. 2011, 37, 1219-1225. 19
ACS Paragon Plus Environment
Environmental Science & Technology
Page 20 of 21
429
(17) Chen, Y.; Han, Y. H.; Cao, Y.; Zhu, Y. G.; Rathinasabapathi, B.; Ma, L. Q. Arsenic transport in rice and
430
biological solutions to reduce arsenic risk from rice. Front. Plant Sci. 2017, 8, 268.
431
(18) Catarecha, P.; Segura, M. D.; Franco-Zorrilla, J. M.; Garcia-Ponce, B.; Lanza, M.; Solano, R.; Paz-Ares, J.;
432
Leyva, A. A mutant of the Arabidopsis phosphate transporter PHT1;1 displays enhanced arsenic accumulation.
433
Plant Cell 2007, 19, 1123-1133.
434
(19) Wang, P.; Zhang, W.; Mao, C.; Xu, G.; Zhao, F. J. The role of OsPT8 in arsenate uptake and varietal
435
difference in arsenate tolerance in rice. J Exp. Bot. 2016, 67, 6051-6059.
436
(20) Gonzalez, E.; Solano, R.; Rubio, V.; Leyva, A.; Paz-Ares, J. PHOSPHATE TRANSPORTER TRAFFIC
437
FACILITATOR1 is a plant-specific SEC12-related protein that enables the endoplasmic reticulum exit of a
438
high-affinity phosphate transporter in Arabidopsis. Plant Cell 2005, 17, 3500-3512.
439
(21) Kamiya, T.; Islam, R.; Duan, G.; Uraguchi, S.; Fujiwara, T. Phosphate deficiency signaling pathway is a
440
target of arsenate and phosphate transporter OsPT1 is involved in As accumulation in shoots of rice. Soil Sci.
441
Plant Nutr. 2013, 59, 580-590.
442
(22) Cao, Y.; Sun, D.; Ai, H.; Mei, H.; Liu, X.; Sun, S.; Xu, G.; Liu, Y.; Chen, Y.; Ma, L. Q. Knocking out
443
OsPT4 gene decreases arsenate uptake by rice plants and inorganic arsenic accumulation in rice grains. Environ.
444
Sci. Technol. 2017, 51, 12131-12138.
445
(23) Wu, Z.; Ren, H.; McGrath, S. P.; Wu, P.; Zhao, F. J. Investigating the contribution of the phosphate
446
transport pathway to arsenic accumulation in rice. Plant Physiol. 2011, 157, 498-508.
447
(24) Ma, L. Q.; Komar, K. M.; Tu, C.; Zhang, W. H.; Cai, Y.; Kennelley, E. D. A fern that hyperaccumulates
448
arsenic - A hardy, versatile, fast-growing plant helps to remove arsenic from contaminated soils. Nature 2001,
449
409, 579.
450
(25) Han, Y.-H.; Liu, X.; Rathinasabapathi, B.; Li, H.-B.; Chen, Y.; Ma, L. Q. Mechanisms of efficient As
451
solubilization in soils and As accumulation by As-hyperaccumulator Pteris vittata. Environ. Pollut. 2017, 227,
452
569-577.
453
(26) Lessl, J. T.; Ma, L. Q. Sparingly-soluble phosphate rock induced significant plant growth and arsenic
454
uptake by Pteris vittata from three contaminated soils. Environ Sci. Technol. 2013, 47, 5311-5318.
455
(27) Lessl, J. T.; Ma, L. Q.; Rathinasabapathi, B.; Guy, C. Novel phytase from Pteris vittata resistant to arsenate,
456
high temperature, and soil deactivation. Environ Sci. Technol. 2013, 47, 2204-2211.
457
(28) Fu, J. W.; Liu, X.; Han, Y. H.; Mei, H.; Cao, Y.; de Oliveira, L. M.; Liu, Y.; Rathinasabapathi, B.; Chen, Y.;
458
Ma, L. Q. Arsenic-hyperaccumulator Pteris vittata efficiently solubilized phosphate rock to sustain plant growth
459
and As uptake. J. Hazard. Mater. 2017, 330, 68-75.
460
(29) DiTusa, S. F.; Fontenot, E. B.; Wallace, R. W.; Silvers, M. A.; Steele, T. N.; Elnagar, A. H.; Dearman, K. M.;
461
Smith, A. P. A member of the Phosphate transporter 1 (Pht1) family from the arsenic-hyperaccumulating fern
462
Pteris vittata is a high-affinity arsenate transporter. New Phytol. 2016, 209, 762-772.
463
(30) Indriolo, E.; Na, G.; Ellis, D.; Salt, D. E.; Banks, J. A. A vacuolar arsenite transporter necessary for arsenic
464
tolerance in the arsenic hyperaccumulating fern Pteris vittata is missing in flowering plants. Plant Cell 2010, 22,
465
2045-2057.
466
(31) Chen, Y.; Xu, W.; Shen, H.; Yan, H.; Xu, W.; He, Z.; Ma, M. Engineering arsenic tolerance and
467
hyperaccumulation in plants for phytoremediation by a PvACR3 transgenic approach. Environ. Sci. Technol.
468
2013, 47, 9355-9362.
469
(32) He, Z.; Yan, H.; Chen, Y.; Shen, H.; Xu, W.; Zhang, H.; Shi, L.; Zhu, Y. G.; Ma, M. An aquaporin PvTIP4;1
470
from Pteris vittata may mediate arsenite uptake. New Phytol. 2016, 209, 746-761. 20
ACS Paragon Plus Environment
Page 21 of 21
Environmental Science & Technology
471
(33) Gietz, R. D.; Schiestl, R. H. Transforming yeast with DNA. Methods Mol. Cell. Biol. 1995, 5, 255-269.
472
(34) Curtis, I. S.; Davey, M. R.; Power, J. B. Leaf disk transformation. Methods Mol. Biol. 1995, 44, 59-70.
473
(35) Gallois, P.; Marinho, P. Leaf disk transformation using Agrobacterium tumefaciens-expression of
474
heterologous genes in tobacco. Methods Mol. Biol. 1995, 49, 39-48.
475
(36) Zhou, J.; Jiao, F.; Wu, Z.; Li, Y.; Wang, X.; He, X.; Zhong, W.; Wu, P. OsPHR2 is involved in
476
phosphate-starvation signaling and excessive phosphate accumulation in shoots of plants. Plant Physiol. 2008,
477
146, 1673-1686.
478
(37) Chen, Y.; Fu, J. W.; Han, Y. H.; Rathinasabapathi, B.; Ma, L. Q. High As exposure induced substantial
479
arsenite efflux in As-hyperaccumulator Pteris vittata. Chemosphere 2016, 144, 2189-2194.
480
(38) Lopez-Arredondo, D. L.; Leyva-Gonzalez, M. A.; Gonzalez-Morales, S. I.; Lopez-Bucio, J.;
481
Herrera-Estrella, L. Phosphate nutrition: improving low-phosphate tolerance in crops. Annu. Rev. Plant Biol.
482
2014, 65, 95-123.
483
(39) Nussaume, L.; Kanno, S.; Javot, H.; Marin, E.; Pochon, N.; Ayadi, A.; Nakanishi, T. M.; Thibaud, M. C.
484
Phosphate import in plants: focus on the PHT1 transporters. Front. Plant Sci. 2011, 2, 83.
485
(40) Rae, A. L.; Cybinski, D. H.; Jarmey, J. M.; Smith, F. W. Characterization of two phosphate transporters
486
from barley; evidence for diverse function and kinetic properties among members of the Pht1 family. Plant Mol.
487
Biol. 2003, 53, 27-36.
488
21
ACS Paragon Plus Environment