Document not found! Please try again

Phosphate transporter PvPht1;2 enhances phosphorus accumulation

9 hours ago - Under P-deficient condition, expressing PvPht1;2 increased the biomass by 27–67% in transgenic tobacco. Based on radiolabeled P (32P),...
3 downloads 9 Views 1MB Size
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