Using Synchrotron-Based Approaches To Examine the Foliar

Nov 1, 2017 - The effects of foliar-applied ZnO nanoparticles (ZnO NPs) and ZnSO4 on the winter wheat (Triticum aestivum L.) grain yield and grain qua...
0 downloads 5 Views 3MB Size
Subscriber access provided by CORNELL UNIVERSITY LIBRARY

Article

Using synchrotron-based approaches to examine the foliar application of ZnSO4 and ZnO nanoparticles for field-grown winter wheat Teng Zhang, Hongda Sun, Zhiyuan Lv, Lili Cui, Hui Mao, and Peter M Kopittke J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.7b04153 • Publication Date (Web): 01 Nov 2017 Downloaded from http://pubs.acs.org on November 7, 2017

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 free 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 accessible to all readers and 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.

Journal of Agricultural and Food Chemistry 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 41

Journal of Agricultural and Food Chemistry

1

Using synchrotron-based approaches to examine the foliar application of ZnSO4 and

2

ZnO nanoparticles for field-grown winter wheat

3

Teng Zhang1, 2, Hongda Sun1, Zhiyuan Lv1, Lili Cui1, Hui Mao1, 2, *, Peter M. Kopittke3

4

1

5 6 7 8 9

College of Natural Resources and Environment, Northwest A&F University, Yangling,

712100, Shaanxi, China 2

Key Laboratory of Plant Nutrition and the Agri-environment in Northwest China, Ministry

of Agriculture, Yangling, 712100, Shaanxi, China 3

School of Agriculture and Food Sciences, The University of Queensland, St. Lucia,

Queensland 4072, Australia

10

*

11

Address: College of Natural Resources and Environment, Northwest A&F University,

12

Corresponding author: Hui Mao

Yangling, 712100, Shaanxi, China

13

Tel.: +86 29 8708 0055; Fax: +86 29 8708 0055

14

E-mail: [email protected]

1

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

15

ABSTRACT

16

The effects of foliar-applied ZnO nanoparticles (NPs) and ZnSO4 on winter wheat

17

(Triticum aestivum L.) grain yield and grain quality were studied under field conditions, with

18

the distribution and speciation of Zn within the grain examined using synchrotron-based

19

X-ray fluorescence microscopy and X-ray absorption spectroscopy. Although neither of the

20

two Zn compounds improved grain yield or quality, both increased the grain Zn concentration

21

(average increments were 5 and 10 mg/kg for ZnSO4 and ZnO NPs treatments, respectively).

22

Across all treatments, this Zn was mainly located within the aleurone layer and crease of the

23

grain, although the application of ZnO NPs also slightly increased Zn within the endosperm.

24

This Zn within the grain was found to be present as Zn phosphate, regardless of the form in

25

which the Zn was applied. These results indicate that the foliar-application of ZnO NPs

26

appears to be a promising approach for Zn bio-fortification as required to improve human

27

health.

28 29

KEYWORDS: ZnO nanoparticles, foliar, wheat, Zn biofortification, field experiment, X-ray

30

absorption spectroscopy, X-ray fluorescence microscopy

31

2

ACS Paragon Plus Environment

Page 2 of 41

Page 3 of 41

Journal of Agricultural and Food Chemistry

32

INTRODUCTUION

33

Zinc (Zn) is an essential micronutrient for the growth of plants, animals, and humans.

34

However, Zn deficiency is widespread due to its inherently low concentration and poor

35

bio-availability in a range of soils, leading to an inadequate dietary intake.1 Indeed,

36

approximately 50 % of the world’s important agricultural soils are deficient in Zn,2 with Zn

37

deficiency being one of the most widespread public health problems.3 Worldwide, Zn

38

deficiency ranks eleventh most important of the factors causing illness and disease, being fifth

39

most important in developing countries.4 Worldwide, approximately one third of the human

40

population has an inadequate dietary intake of Zn, causing a loss of 28 million life-years

41

annually.5-6

42

To address this problem, the agronomic and genetic biofortification of Zn are of

43

increasing interest. Although the genetic biofortification of crops is a sustainable and

44

cost-effective approach, it is suitable only for the longer-term. In contrast, the application of

45

Zn-containing fertilizers is a suitable approach for the short-term. Application of Zn fertilizers,

46

either to soils or directly to the leaves, can improve the Zn nutrition of crops and further

47

protect human health. Traditionally, bulk Zn sulfate (ZnSO4) has been used to overcome Zn

48

deficiency, but fertilization using ZnSO4 does not always result in the desired increase in

49

tissue Zn concentrations.7 Thus, it is useful to consider if novel Zn-containing compounds are

50

potentially more efficient in improving the Zn status of the plant. One such compound is

51

Zn-containing nanoparticles, which are of particular interest in the present study. Indeed, with

52

the development of nanotechnology and the increasing use of nanoparticles, the use of

53

nano-fertilizers is gaining increased attention.8-9 It is estimated that the annual value of 3

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

54

nanotechnology related products is expected to reach US$3 trillion by 2020.10 Among these

55

nanomaterials are ZnO nanoparticles (ZnO NPs) which are already used widely in sunscreen

56

products, cosmetics, semiconductors, catalysts, solar cells and pharmaceuticals. Due to their

57

smaller size, NPs have many unique properties, including a large surface area and higher

58

reactivity compared to particles of larger size.11

59

Nanoparticles potentially provide an option for not only improving crop nutrition but

60

also for reducing adverse environmental outcomes.12 Zhao et al.13-14 reported that the

61

application of ZnO NPs to soil increased the Zn content of tissues of cucumber (Cucumis

62

sativus) and maize (Zea mays). In addition, in contrast to bulk ZnO, foliar application of ZnO

63

NPs significantly increased Zn concentration in tissues of sunflower (Helianthus annuus L.).15

64

The foliar application of fertilizers is of particular interest for alkaline soils, where Zn applied

65

directly to the soil is rapidly converted into forms that are unavailable for plant roots.16

66

Furthermore, the rates of Zn applied to soils are generally substantially greater than those

67

applied to the foliage.17-19

68

Recently, synchrotron-based techniques, including X-ray fluorescence microscopy

69

(µ-XRF) and X-ray absorption spectroscopy (XAS), have been used increasingly for the in

70

situ study of biological samples, both to investigate elemental distribution and speciation.20-21

71

For example, Peng et al.22 examined the distribution and speciation of Cu and Zn in grains of

72

rice (Oryza sativa L.) when the plants were supplied with CuO NPs in a glasshouse pot

73

experiment. However, we are aware of only a few studies that have used synchrotron-based

74

approaches for the in situ analysis of the distribution or speciation of Zn in plant tissues

75

following the foliar-application of Zn compounds. For example, Ajiboye et al.23 used µ-XRF 4

ACS Paragon Plus Environment

Page 4 of 41

Page 5 of 41

Journal of Agricultural and Food Chemistry

76

to examine the distribution of Zn in grains of wheat following the foliar-application of ZnSO4,

77

finding that the Zn was mainly present in the aleurone layer, crease tissue, and to a lesser

78

extent in endosperm. In addition, Du et al.24 used µ-XRF to examine changes in Zn

79

distribution in leaves following foliar-application of ZnSO4 and Zn hydroxide nitrate to

80

tomato (Solanum lycopersicum) and citrus (Citrus reticulatus). However, it remains unknown

81

whether the speciation of Zn in the grains of wheat differs between plants depending upon the

82

form of Zn supplied. In this regard, the use of synchrotron-based XAS can assist in

83

understanding the role of Zn fertilizer in Zn bio-fortification, as required to improve human

84

health.

85

The aim of the present study was to use a field experiment to examine how the

86

foliar-application of ZnO NPs influenced plant behavior, including the Zn concentration of

87

wheat grain Zn. Synchrotron-based XAS was used to determine the speciation of Zn within

88

the grain following this application of ZnO NPs and compared to plants supplied with ZnSO4.

89

In a similar manner, synchrotron-based µ-XRF was used to compare the distribution of Zn

90

within the wheat grain. Finally, the concentrations of proteins, starch and carbohydrates were

91

also examined.

92 93

MATERIALS AND METHODS

94

Preparation of ZnO NPs and ZnSO4. The ZnO NPs (purity 99.6 %) was obtained from

95

Hongsheng Material Sci & Tech Co. (China), and the ZnSO4·7H2O from Klamar (China). The

96

surface area of the ZnO NPs was calculated by the multipoint Brunauer-Emmett-Teller (BET)

97

method.25 The morphology of the ZnO NPs was examined in deionized (DI) water using 5

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

98

transmission electron microscopy (TEM, JEOL 100CX, Japan), with the hydrodynamic size

99

examined using dynamic light scattering (DLS, Wyatt Technology Dynapro Titan TC, US).

100

Site Description and Experiment Design. The experimental field site is located in

101

Yujiagong Village, Yongshou County, Shaanxi Province, China (latitude 34°49′ N, longitude

102

108°11′ E, elevation 1127 m above sea level), being a typical Zn deficient (DTPA-Zn < 0.50

103

mg/kg) area within the Loess Plateau (Table 1). The soil at the trial site is classified as

104

Earth-cumuli-Orthic Anthrosols (Udic Haplustalf in the US Soil Taxonomy). The annual

105

precipitation is 610 mm and the average annual temperature is 10 °C. Approximately 65 % of

106

the annual precipitation falls between July and September.

107

The experimental design was a randomized complete block with four replicates. The

108

three treatments consisted of: no Zn fertilizer (CK), foliar-applied ZnO NPs (0.2 % w/v, i.e. 2

109

g/L) at a rate of 1.2 kg/ha (FZnO), and foliar-applied ZnSO4·7H2O (0.7 % w/v, i.e. 7 g/L) at a

110

rate of 4.2 kg/ha (FZn). Therefore, 12 plots were arranged, with each having an area of 4 m2

111

(2 m × 2 m). The nanoparticles that were applied did not have a surface coating. The foliar

112

application rates of ZnO NPs and ZnSO4·7H2O were calculated to correspond to the same

113

level of Zn, being 0.96 kg Zn ha-1, with the rate at which ZnSO4·7H2O applied corresponding

114

to the recommended rate for this region.7 In stem elongation and early milk stages, the two Zn

115

compounds were sprayed with a rate of half, respectively. In addition to this foliar-application

116

of Zn, basal nutrients were applied to the soil prior to sowing, with 120 kg N ha-1 (as urea)

117

and 90 kg P2O5 ha-1 (as superphosphate) applied to each plot. These field experiments were

118

conducted during winter from September 20 to June 15 in 2015-2016 (first growing season,

119

Year 1) and from September 22 to June 18 in 2016-2017 (second growing season, Year 2) 6

ACS Paragon Plus Environment

Page 6 of 41

Page 7 of 41

Journal of Agricultural and Food Chemistry

120

with wheat cultivar luohan 6. These same treatments were applied in both cropping seasons.

121

Grain Yield and Zn Concentration. The wheat grain was harvested in mid-June of

122

each year, with yield determined. Some of the samples were thoroughly washed with DI water

123

and oven-dried at 65 °C for 48 h. Then the dried grains were ground using a ball miller

124

(RETSCH MM400, Germany) and digested with 5 mL HNO3 and 1 mL H2O2 by a microwave

125

digestion system (PreeKem WX-800, Shanghai, China). A standard wheat flour GBW10046

126

(GSB-24) was also used for quality control, with the average recovery being 93 %. The bulk

127

Zn concentration of the grain was determined by using graphite furnace atomic absorption

128

spectrophotometry (HITACHI Z2000, Japan). To examine the dissolution of the ZnO NPs, the

129

concentration of soluble Zn concentration was examined in supernatants of 2 g/L ZnO NPs

130

suspensions as described by Lin and Xing26. The suspensions were first prepared using DI

131

water before being sonicated for 30 min (SHUMEI KQ-500DE, Zhejiang, China).

132

Determination of Total Soluble Sugars and Starch. The soluble sugars and starch were

133

extracted as described by Verma and Dubey.27 For soluble sugars, 0.1 g of the ground grain

134

was homogenized in 10 mL of 80 % ethanol and placed in a water bath heated to 80 °C for 30

135

min. Thereafter, the contents were centrifuged at 22,000 g for 20 min. This process was

136

repeated three times, with the three supernatants combined. Thereafter, the residue was

137

removed for the measurement of starch. Briefly, the residue was oven-dried at 80 °C for 24 h,

138

then 2 mL of DI water was added to boil the dried residue with a water bath for 15 min. The

139

contents were mixed with 2 mL of concentrated H2SO4, and stirred with a glass rod for 15 min.

140

The extracts were centrifuged at 3000 g for 20 min, and the extraction performed with 50 %

141

H2SO4. The supernatants were combined, and the content of soluble sugars and starch were 7

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

142

determined as described by Dubois and Gilles.28

143

Determination of Crude Protein and Components. The protein components were

144

extracted as described by Chen and Bushuk.29 Briefly, 0.5 g of the ground grain material was

145

extracted using: DI water, 0.5 M NaCl, 70 % ethanol, and 0.05 M acetic acid. The albumin,

146

globulin, prolamin, and glutelin were obtained sequentially, with their content determined as

147

described by Bradford.30 The crude protein content was measured by DigiPREP TKN Systems

148

(FOSS KjeltecTM 8400, Sweden) with a coefficient of 5.7.

149

µ-XRF Analysis of Elemental Distribution. The wheat grain was washed with DI water

150

three times before being placed in liquid nitrogen for 30 min. Samples were transversely

151

sectioned (150 µm thick) with a Lecia CM1950 cryomicrotome at -20 °C with Tissue Tek

152

(Sakura Finetek USA, Torrance, CA) embedding medium. Then a series of thin sections were

153

obtained and placed on Kapton tape. Samples were freeze-dried for 1 h (Telstar

154

LYOQUEST-85 plus, Spain) at -53 °C and 0.140 mBar pressure.

155

The µ-XRF mapping was conducted at beamline 4W1B of the Beijing Synchrotron

156

Radiation Facility (BSRF). The beam was focused to 50 µm × 50 µm (vertical × horizontal)

157

using Kirkpatrick-Baez mirrors and a polycapillary lens. The two dimensional mapping was

158

conducted at an incident energy of 15 keV in step-mode, with a step size of 500 µm. The XRF

159

signal was collected using a Si (Li) solid state detector with a live time of 60 s. The XRF data

160

were analyzed using the PyMCA software.31

161

Bulk XAS Analyses of Zn Speciation. The grain samples were placed in liquid nitrogen

162

for 30 min after harvest and freeze-dried for 72 h. Afterwards, the grain samples were

163

homogenized using an agate mortar and pestle, formed into pellets, placed on Kapton film, 8

ACS Paragon Plus Environment

Page 8 of 41

Page 9 of 41

Journal of Agricultural and Food Chemistry

164

and placed on sample holders to allow for analysis. The X-ray absorption near edge structure

165

(XANES) spectra were collected at the Zn K-edge (9.659 keV) at the XAS beamline of the

166

Australian Synchrotron in fluorescence mode with a 100-element solid-state Ge detector. To

167

minimize beam-induced artifacts and thermal disorder, all samples were analyzed in a cryostat

168

(ca. 12 K, liquid helium). The spectra were calibrated using a Zn foil measured

169

simultaneously in transmission.

170

In addition to the grain samples, XANES spectra were also collected for eight standard

171

compounds, being ZnO NPs, Zn phosphate (Zn3(PO4)2), Zn phytate, Zn cysteine, Zn histidine,

172

Zn citrate, Zn oxalate, and aqueous (Zn2+), as described previously.32 The XANES spectra

173

were processed using ATHENA version 0.8.56, with linear combination fitting (LCF) used for

174

sitting the sample spectra.

175

Data Analysis. Statistical analyses were performed using SPSS (Version 19.0, SPSS

176

Inc.). Means were compared using analyses of variance (ANOVA), with results reported as

177

mean values ± standard deviation (SD). A probability level of p < 0.05 was considered as

178

significant in all measured traits.

179 180

RESULTS AND DISCUSSION

181

Characterization of ZnO NPs. The BET surface area of the ZnO NPs was measured to

182

be 52 m2/g. Using TEM, the ZnO NPs were found to be nearly spherical to oblong in shape,

183

with some aggregation observed due to drying on the TEM grid (Figure 1A). From the TEM

184

micrographs, the average diameter was measured for > 150 single particles, with the average

185

size being 20 ± 5 nm. These measurements from TEM are in agreement with the data 9

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

186

provided by the manufacturer. The DLS analysis was used to examine hydrodynamic size,

187

with a mean hydrodynamic diameter of 406 nm (Figure 1B).

188

Effects of the Foliar-application of Zn on Grain Yield and Zn Concentration.

189

Overall, average yield was higher in Year 1 (7,817 kg/ha) than in Year 2 (5,210 kg/ha) (Table

190

2). However, the foliar-application of Zn compounds did not increase yield, either as ZnSO4

191

or as ZnO NPs (Table 2). In contrast, the concentration of Zn within the grain was increased

192

significantly by the foliar-application of both of these compounds. Specifically, the grain Zn

193

concentration increased from 18 mg/kg in Year 1 and 24 mg/kg in Year 2 in the control, to 21

194

mg/kg in Year 1 and 30 mg/kg in Year 2 in the ZnSO4 treatment, and to 27 mg/kg in Year 1

195

and 35 mg/kg in Year 2 in the ZnO NPs treatment (Table 2).

196

The observation in the present study that the foliar application of Zn did not increase

197

yield is in general agreement with previous studies, although some studies have also reported

198

that yield does actually increase upon foliar fertilization.33-34 For example, studying seven

199

countries, Ram et al.34 reported that foliar-application of Zn generally increased yield in the

200

trial site in Pakistan, but not in India, Brazil, China, Turkey, or Zambia – this pattern of grain

201

yield response was not related to concentrations of DTPA-Zn in the soil. In a similar manner,

202

Zhang et al.17 reported that foliar application of ZnSO4·7H2O did not increase wheat grain

203

yield in China. In contrast to the grain yield, the foliar-application of Zn compounds

204

significantly increased the grain Zn concentration, with these findings being similar to those

205

reported previously in wheat.33-35 We noted, however, that the application of ZnO NPs

206

increased the grain Zn concentration to a greater extent than did the application of ZnSO4,

207

with average values being 21 mg/kg for the control, 26 mg/kg for ZnSO4, and 31 mg/kg for 10

ACS Paragon Plus Environment

Page 10 of 41

Page 11 of 41

Journal of Agricultural and Food Chemistry

208

ZnO NPs (Table 2). Cakmak et al.36 and Pfeiffer et al.37 have stated that the increase in the Zn

209

concentration of the grain should be ≥ 10 mg/kg to have a measurable biological influence on

210

human health. Thus, in the present study, the increase in the Zn concentration in the grain for

211

the ZnO NPs treatment is similar to that reported to be beneficial by Cakmak et al.36 and

212

Pfeiffer et al.37 . Comparing against control, the foliar-application of ZnSO4 increased grain

213

Zn concentration by 3 mg/kg in Year 1 and 6 mg/kg in Year 2, while foliar-applied ZnO NPs

214

increased concentrations by 9 mg/kg in Year 1 and 11 mg/kg in Year 2, thereby indicating the

215

greater efficacy of ZnO NPs. It is possible that the higher efficiency of the ZnO NPs relative

216

to the ZnSO4 is due to the smaller size effect of the nanoparticles which increases adhesion on

217

the leaf surface,38 with the slow dissolution of the ZnO NPs (the concentration of soluble Zn

218

in a ZnO NP suspension was measured to be 4.2 mg/L), with this then serving as a sustained

219

Zn pool to provide Zn nutrition for plant growth. However, further experiments would be

220

required to examine the adhesion of the NPs to the leaf surface.

221

In the present study, the ZnSO4 and ZnO NPs were applied in stem elongation and milk

222

stages, with these having been identified previously as the being the best for the

223

bio-fortification of Zn.23, 36 However, whilst we found that the ZnO NPs were more effective

224

for increasing the grain Zn concentration, the grain Zn concentrations for both the ZnO NPs

225

(average of 31 mg/kg) and ZnSO4 (average of 26 mg/kg) were < 40 mg/kg (with this being

226

the value recommended by Food and Agriculture Organization of the United Nations), and so

227

further work is required in this regard.

228

Effects of ZnO NPs and ZnSO4 on Grain Quality Factors. It was hypothesized that

229

the foliar fertilization of both ZnSO4 and ZnO NPs would improve grain yield and Zn 11

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 12 of 41

230

concentration, as well as improving grain quality. Starch and sugars have important effects on

231

grain quality, and are the major carbohydrate components in wheat grains, being mostly stored

232

in the endosperm.14, 39 The grain protein content is also an important factor in determining

233

quality.40 Normally, prolamin and glutelin components account for 66-87 % of the total

234

protein in wheat grain. Although the proportions of albumin and globulin are comparatively

235

small, they are rich in lysine and have higher nutritional value. In the present study, we

236

examined the effects of the foliar-application of ZnO NPs and ZnSO4 on these grain quality

237

factors (Tables 3 and 4). Neither the application of ZnO NPs or ZnSO4 markedly influenced

238

any of the measured grain quality parameters, indicating that although the foliar application of

239

Zn increased grain Zn concentrations, it did not alter concentrations of carbohydrates

240

(protein).

241

The finding that the foliar-application of Zn did not impact upon grain quality is in

242

general agreement with previous studies.41-42 For example, although Li et al.43 also found that

243

the foliar-application of Zn increased the Zn concentration of the grain, it had no influence on

244

the grain protein concentration. However, where the foliar-application of Zn increases yield, it

245

is possible that this will also impact upon grain quality. For example, in a field experiment,

246

Amiri et al.44 found an inverse relationship between the grain Zn concentration, protein

247

concentration, and grain yield. Specifically, the addition of Zn decreased the protein

248

concentration due to a dilution effect resulting from increased yield, but the addition of Zn did

249

not increase yield in the present study (Table 2).

250 251

Synchrotron

µ-XRF

Analysis

of

Zn

Localization

in

Wheat

Grains.

Synchrotron-based µ-XRF was used for the in situ examination of the distribution of Zn in 12

ACS Paragon Plus Environment

Page 13 of 41

Journal of Agricultural and Food Chemistry

252

sections of wheat grain. In all three treatments, the Zn was mainly found within the aleurone

253

layer and the crease region (Figures 2 and 3). These results are in agreement with the studies

254

of both De Brier et al.20 and Ajiboye et al.23 who also examined wheat grain, with it being

255

reported that the Zn within the grain was mainly present within the aleurone and crease.

256

However, as expected based upon bulk measurements (Table 2), we found that the

257

concentration of Zn within these tissues differed between treatments, being highest for the

258

ZnO NPs treatment and lowest in the control. Of particular importance, it was also found that

259

the Zn concentration in the endosperm increased slightly for the ZnO NPs treatment (Figures

260

2 and 3). The endosperm fraction of the grain is widely consumed worldwide and an increase

261

in the endosperm Zn concentration would be important for human nutrition. In a similar

262

manner, Cakmak et al.36 examined Zn distribution within wheat grain using laser ablation

263

inductively coupled plasma mass spectrometry (LA-ICP-MS), also finding that foliar-applied

264

Zn could potentially increase the Zn concentration within the endosperm. Recently, using

265

µ-XRF analyses, Ajiboye et al.23 also found similar result, with the Zn concentration of the

266

endosperm increasing slightly. Indeed, It is known that Zn is primarily transported from the

267

crease vascular parenchyma into the nucellar projection and modified aleurone, then

268

distributes to the aleurone layer, the endosperm and the embryo.20, 45 However, due to inherent

269

barriers of aleurone layer (with transported Zn, Fe and other elements occurring as phosphates

270

in this layer), this limits Zn from entering the endosperm.46-47

271

Although the production of wheat flour for human consumption results in the removal of

272

the seed coat, embryo, and the aleurone layer,48 the increased Zn observed in the crease region

273

and the endosperm in the present study (along the whole vertical section of wheat grains, 13

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

274

Figures 2 and 3) would presumably result in a substantial improvement in Zn delivery for

275

human health, especially following the foliar-application of ZnO NPs.

276

Speciation of Zn within Wheat Grains. First, we compared the Zn K-edge spectra of

277

the various standard compounds (Figure 4A). It was noted that these spectra had various

278

distinctive features, including the (i) energy corresponding to the white-line peak, (ii) height

279

of the white-line peak, and (iii) presence of other spectral features. First, the energy

280

corresponding to the white-line peak were examined. For all forms of Zn complexed by

281

carboxyl groups (such as Zn citrate and Zn oxalate) and uncomplexed Zn2+ (i.e. the Zn(NO3)2

282

solution), the white-line peak was found to correspond to an energy of 9,669 eV. However,

283

differences were found for the remaining standard compounds examined, being at ca. 9,668.4

284

eV for Zn histidine, 9,667 eV for Zn phosphate and Zn phytate, and at 9,665 eV for Zn

285

cysteine, whilst ZnO NPs had a shoulder at 9,665 eV and a peak at ca. 9,671 eV. Next, the

286

height of the white-line peak was considered. Again, it was found that the spectra were similar

287

in this regard for all forms of Zn complexed by carboxyl groups and for uncomplexed Zn2+,

288

with these spectra having a comparatively high peak. Indeed, in approximate descending

289

order of peak height: Zn-carboxyl / free Zn2+ > ZnO NPs ~ Zn phytate ~ Zn histidine > Zn

290

phosphate > Zn cysteine. Thus, it was clear that the spectra for the various forms of Zn

291

complexed by carboxyl groups and the spectrum for uncomplexed Zn2+ were visually similar,

292

and it was not possible to distinguish between these various forms of Zn.

293

Next, we examined the grain samples. It was firstly noted that the spectra from all wheat

294

grain samples were similar in appearance (Figure 4B), with the foliar application of Zn not

295

influencing the speciation of Zn in the grains regardless of the form in which the Zn was 14

ACS Paragon Plus Environment

Page 14 of 41

Page 15 of 41

Journal of Agricultural and Food Chemistry

296

added. Next, it was noted that the height of the white-line peak and its energy (9,667 eV) for

297

the samples corresponded most closely with that of Zn associated with P (i.e. either Zn

298

phosphate or Zn phytate) (Figure 4C). However, the spectrum was not identical to that of Zn

299

phosphate, indicating that although likely dominated by Zn phosphate, some Zn was also

300

present in other forms. Indeed, using linear combination fitting (LCF), it was estimated that

301

70-80 % of the Zn was present as Zn phosphate but that 20-30 % was present as other forms.

302

However, the form of the remaining 20-30 % of the Zn remains unclear, with several different

303

compounds yielding similar R-factors. Certainly, it was apparent that the Zn in the wheat

304

grains was not present as ZnO NPs despite the foliar application of this compound, with the

305

spectrum for the grain differing markedly from the spectrum for ZnO NPs (Figures 4A and

306

4B).

307

The data suggest that the uptake of Zn in leaves treated with ZnO NPs occurred as

308

soluble Zn rather than as NPs per se. This result is consistent with the soil application of ZnO

309

NPs in cowpea (Vigna unguiculata) and wheat,9, 11 as well as with the addition of ZnO NPs to

310

the nutrient solution for growth of maize.49 Although several studies have examined the

311

potential uptake of NPs by roots,11,

312

absorption through leaves.8 Thus, we hypothesize that the dissolution of the ZnO NPs on the

313

leaf surface (the concentration of Zn in a saturated suspension of ZnO NPs being 4.2 mg/L)

314

allowed the movement of soluble Zn across the leaf surface, before being translocated to the

315

grain in a similar manner to that occurring when the Zn was supplied as ZnSO4. In this regard,

316

it is known that Zn in the leaf and stem tissues of wheat can be remobilized and transported

317

into wheat grains during the period of seed formation.36, 51. However, further studies are still

49-50

comparatively few studies have examined their

15

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

318

required in this regard in order to understand the interactions between leaf tissues and NPs.

319

Furthermore, additional studies would also be required to consider any potential adverse

320

effect of ZnO NPs on human health during their application (spraying) within the field by

321

farmers.

322

Another issue that deserves consideration is the observation that Zn was primarily

323

associated with P in all treatments, seemingly largely as Zn phosphate (Figure 4C). The

324

speciation of Zn appears to differ markedly between plant species and between tissues. For

325

example, in seeds of cowpea, Wang et al.9 reported that Zn histidine and Zn cysteine were the

326

dominant compounds. In a soil-based study examining soybean (Glycine max), Zn was found

327

to largely be associated with citrate in the pods.52 In another study, Dimkpa et al.11 examined

328

wheat seedlings grown in sand culture and found that the addition of bulk ZnO, ZnO NPs and

329

Zn2+ resulted in the formation of Zn phosphate (hopeite, Zn3(PO4)2·4H2O) in the shoots of

330

wheat.11 Finally, Hatzack et al.53 and Persson et al.54 both found the accumulation of phytic

331

acid had no effect on Zn, and the Zn was not complexed by phytate in barley (Hordeum

332

vulgare L.) grains.

333

In summary, across the two cropping seasons of the present study, although the foliar

334

application of ZnSO4 and ZnO NPs did not increase grain yield, starch, soluble sugars, or

335

proteins, their application did significantly increased the concentration of Zn in the grain. The

336

magnitude of this increase was greater for ZnO NPs than for ZnSO4, with the increase in Zn

337

concentration for the ZnO NPs treatment (up to 10 mg/kg) being sufficient to have a

338

measurable influence on human health. Using µ-XRF mapping to examine the distribution of

339

Zn within the wheat grains, it was found that Zn was mainly present within the aleurone layer 16

ACS Paragon Plus Environment

Page 16 of 41

Page 17 of 41

Journal of Agricultural and Food Chemistry

340

and within crease region, regardless of treatment. However, for ZnO NPs treatment, the Zn

341

concentration in the endosperm also increased somewhat, with this being particularly

342

important for human Zn nutrition. Although the seed coat, embryo, and aleurone layer are

343

removed for human consumption, the increased Zn within the crease region is also likely to

344

still improve Zn delivery for human health. Furthermore, XANES analysis suggested that

345

although the use of ZnO NPs increased Zn concentrations in the grain, this Zn that

346

accumulated within the grain was not present as ZnO NPs, but rather, it was in the same form

347

as in the two other treatments. To the best of our knowledge, this is the first report of the

348

speciation of Zn in wheat grain following the foliar-application of ZnSO4 and ZnO NPs

349

following growth in field conditions. The foliar-application of ZnO NPs appears to be a

350

promising approach for Zn bio-fortification as required to improve human health, particularly

351

in developing countries.

352 353

ABBREVIATIONS

354

LCF: Linear Combination Fitting

355

µ-XRF: Synchrotron-based X-ray Fluorescence Microscopy

356

XAS: X-ray Absorption Spectroscopy

357

DI water: deionized water

358

ZnO NPs: ZnO nanoparticles

359

TEM: transmission electron microscopy

360

DLS: dynamic light scattering

361

LA-ICP-MS: laser ablation inductively coupled plasma mass spectrometry 17

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

362 363

ACKNOWLEDGEMENTS

364

The staff members at 4W1B beamline of Beijing Synchrotron Radiation Facility,

365

Institute of High Energy Physics, Chinese Academy of Sciences are acknowledged for their

366

support in measurements and data reduction. Components of this research were undertaken on

367

the XAS beamline at the Australian Synchrotron, part of the Australian Nuclear Science and

368

Technology Organisation (ANSTO).

369 370 371

FUNDING The authors gratefully acknowledge the National Natural Science Foundation of China

372

(41571282), the Fundamental Research Funds for the Central Universities (2452015047), the

373

Natural Key Technologies R&D Program (2015BAD23B04), and the Special Fund for

374

Ago-scientific Research in the Public Interest (201503124).

375 376 377

NOTES The authors declare that they have no competing interests.

378

18

ACS Paragon Plus Environment

Page 18 of 41

Page 19 of 41

Journal of Agricultural and Food Chemistry

379

REFERENCES

380

(1) McBeath, T. M.; McLaughlin, M. J. Efficacy of zinc oxides as fertilisers. Plant Soil 2013,

381

374, 843-855.

382

(2) Alloway, B. J.; Graham, R. D.; Stacey, S. P. Micronutrient Deficiencies in Australian Field

383

Crops. In Micronutrient Deficiencies in Global Crop Production, Alloway, B. J., Ed.;

384

Springer: Dordrecht, Netherlands, 2008; pp 63-92.

385

(3) Tulchinsky, T. H. Micronutrient deficiency conditions: global health issues. Public Health

386

Rev. 2010, 32, 243-255.

387

(4) Cakmak, I. Enrichment of cereal grains with zinc: Agronomic or genetic biofortification?

388

Plant Soil 2007, 302, 1-17.

389

(5) Persson, D. P.; de Bang, T. C.; Pedas, P. R.; Kutman, U. B.; Cakmak, I.; Andersen, B.;

390

Finnie, C.; Schjoerring, J. K.; Husted, S. Molecular speciation and tissue compartmentation of

391

zinc in durum wheat grains with contrasting nutritional status. New Phytol. 2016, 211,

392

1255-1265.

393

(6) Caulfield, L. E.; Richard, S. A.; Black, R. E. Undernutrition as an underlying cause of

394

malaria morbidity and mortality in children less than five years old. Am. J. Trop. Med. Hyg.

395

2004, 71, 55-63.

396

(7) Wang, J. W.; Mao, H.; Zhao, H. B.; Huang, D. L.; Wang, Z. H. Different increases in

397

maize and wheat grain zinc concentrations caused by soil and foliar applications of zinc in

398

Loess Plateau, China. Field Crops Res. 2012, 135, 89-96.

399

(8) Wang, P.; Lombi, E.; Zhao, F. J.; Kopittke, P. M. Nanotechnology: A new opportunity in

400

plant sciences. Trends Plant Sci. 2016, 21, 699-712. 19

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

401

(9) Wang, P.; Menzies, N. W.; Lombi, E.; McKenna, B. A.; Johannessen, B.; Glover, C. J.;

402

Kappen, P.; Kopittke, P. M. Fate of ZnO nanoparticles in soils and cowpea (Vigna

403

unguiculata). Environ. Sci. Technol. 2013, 47, 13822-13830.

404

(10) Roco, M. C.; Mirkin, C. A.; Hersam, M. C. Nanotechnology research directions for

405

societal needs in 2020: Summary of international study. J. Nanopart. Res. 2011, 13, 897-919.

406

(11) Dimkpa, C. O.; Latta, D. E.; McLean, J. E.; Britt, D. W.; Boyanov, M. I.; Anderson, A. J.

407

Fate of CuO and ZnO nano- and microparticles in the plant environment. Environ. Sci.

408

Technol. 2013, 47, 4734-4742.

409

(12) Liu, R.; Lal, R. Potentials of engineered nanoparticles as fertilizers for increaseing

410

agronomic productions. Sci. Total Environ. 2015, 514, 131-139.

411

(13) Zhao, L. J.; Sun, Y. P.; Hernandez-Viezcas, J. A.; Hong, J.; Majumdar, S.; Niu, G.;

412

Duarte-Gardea, M.; Peralta-Videa, J. R.; Gardea-Torresdey, J. L. Monitoring the

413

environmental effects of CeO2 and ZnO nanoparticles through the life cycle of corn (Zea

414

mays) plants and in situ µ-XRF mapping of nutrients in kernels. Environ. Sci. Technol. 2015,

415

49, 2921-2928.

416

(14) Zhao, L. J.; Peralta-Videa, J. R.; Rico, C. M.; Hernandez-Viezcas, J. A.; Sun, Y. P.; Niu,

417

G.; Servin, A.; Nunez, J. E.; Duarte-Gardea, M.; Gardea-Torresdey, J. L. CeO2 and ZnO

418

nanoparticles change the nutritional qualities of cucumber (Cucumis sativus). J. Agric. Food

419

Chem. 2014, 62, 2752-2759.

420

(15) Torabian, S.; Zahedi, M.; Khoshgoftar, A. H. Effects of foliar spray of two kinds of zinc

421

oxide on the growth and ion concentration of sunflower cultivars under salt stress. J. Plant

422

Nutr. 2015, 39, 172-180. 20

ACS Paragon Plus Environment

Page 20 of 41

Page 21 of 41

Journal of Agricultural and Food Chemistry

423

(16) Wang, S.; Wang, Z.; Gao, Y.; Liu, L.; Yu, R.; Jin, J.; Luo, L.; Hui, X.; Li, F.; Li, M.

424

EDTA alone enhanced soil zinc availability and winter wheat grain Zn concentration on

425

calcareous soil. Environ. Exp. Bot. 2017, 141, 19-27.

426

(17) Zhang, Y. Q.; Sun, Y. X.; Ye, Y. L.; Karim, M. R.; Xue, Y. F.; Yan, P.; Meng, Q. F.; Cui, Z.

427

L.; Cakmak, I.; Zhang, F. S.; Zou, C. Q. Zinc biofortification of wheat through fertilizer

428

applications in different locations of China. Field Crops Res. 2012, 125, 1-7.

429

(18) Zhao, L. J.; Sun, Y. P.; Hernandez-Viezcas, J. A.; Servin, A. D.; Hong, J.; Niu, G.;

430

Peralta-Videa, J. R.; Duarte-Gardea, M.; Gardea-Torresdey, J. L. Influence of CeO2 and ZnO

431

nanoparticles on cucumber physiological markers and bioaccumulation of Ce and Zn: A life

432

cycle study. J. Agric. Food Chem. 2013, 61, 11945-11951.

433

(19) Mukherjee, A.; Sun, Y. P.; Morelius, E.; Tamez, C.; Bandyopadhyay, S.; Niu, G.; White, J.

434

C.; Peralta-Videa, J. R.; Gardea-Torresdey, J. L. Differential toxicity of bare and hybrid ZnO

435

nanoparticles in green pea (Pisum sativum L.): A Life Cycle Study. Front. Plant Sci. 2015, 6,

436

1242.

437

(20) De Brier, N.; Gomand, S. V.; Donner, E.; Paterson, D.; Smolders, E.; Delcour, J. A.;

438

Lombi, E. Element distribution and iron speciation in mature wheat grains (Triticum aestivum

439

L.) using synchrotron X-ray fluorescence microscopy mapping and X-ray absorption

440

near-edge structure (XANES) imaging. Plant, Cell Environ. 2016, 39, 1835-1847.

441

(21) Weekley, C. M.; Aitken, J. B.; Finney, L.; Vogt, S.; Witting, P. K.; Harris, H. H. Selenium

442

metabolism in cancer cells: the combined application of XAS and XFM techniques to the

443

problem of selenium speciation in biological systems. Nutrients 2013, 5, 1734-1756.

21

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

444

(22) Peng, C.; Xu, C.; Liu, Q.; Sun, L.; Luo, Y.; Shi, J. Fate and transformation of CuO

445

nanoparticles in the soil–rice system during the life cycle of rice plants. Environ. Sci. Technol.

446

2017, 51, 4907-4917.

447

(23) Ajiboye, B.; Cakmak, I.; Paterson, D.; de Jonge, M. D.; Howard, D. L.; Stacey, S. P.;

448

Torun, A. A.; Aydin, N.; McLaughlin, M. J. X-ray fluorescence microscopy of zinc

449

localization in wheat grains biofortified through foliar zinc applications at different growth

450

stages under field conditions. Plant Soil 2015, 392, 357-370.

451

(24) Du, Y.; Kopittke, P. M.; Noller, B. N.; James, S. A.; Harris, H. H.; Xu, Z. P.; Li, P.;

452

Mulligan, D. R.; Huang, L. In situ analysis of foliar zinc absorption and short-distance

453

movement in fresh and hydrated leaves of tomato and citrus using synchrotron-based X-ray

454

fluorescence microscopy. Ann. Bot. 2015, 115, 41-53.

455

(25) Yang, K.; Zhu, L.; Xing, B. Adsorption of polycyclic aromatic hydrocarbons by carbon

456

nanomaterials. Environ. Sci. Technol. 2006, 40, 1855-1861.

457

(26) Lin, D. H.; Xing, B. S. Phytotoxicity of nanoparticles: Inhibition of seed germination and

458

root growth. Environ. Pollut. 2007, 150, 243-250.

459

(27) Verma, S.; Dubey, R. Effect of cadmium on soluble sugars and enzymes of their

460

metabolism in rice. Biol. Plant. 2001, 44, 117-123.

461

(28) DuBois, M.; Gilles, K. A.; Hamilton, J. K.; Rebers, P. t.; Smith, F. Colorimetric method

462

for determination of sugars and related substances. Anal. Chem. 1956, 28, 350-356.

463

(29) Chen, C. H.; Bushuk, W. Nature of proteins in triticale and its parental species: I.

464

solubility characteristics and amino acid composition of endosperm proteins. Can. J. Plant Sci.

465

1970, 50, 9-14. 22

ACS Paragon Plus Environment

Page 22 of 41

Page 23 of 41

Journal of Agricultural and Food Chemistry

466

(30) Bradford, M. M. A rapid and sensitive method for the quantitation of microgram

467

quantities of protein utilizing the principle of protein-dye binding. Anal. Biochem. 1976, 72,

468

248-254.

469

(31) Solé, V. A.; Papillon, E.; Cotte, M.; Walter, P.; Susini, J. A multiplatform code for the

470

analysis of energy-dispersive X-ray fluorescence spectra. Spectrochim. Acta, Part B 2007, 62,

471

63-68.

472

(32) Kopittke, P. M.; Menzies, N. W.; de Jonge, M. D.; McKenna, B. A.; Donner, E.; Webb, R.

473

I.; Paterson, D. J.; Howard, D. L.; Ryan, C. G.; Glover, C. J.; Scheckel, K. G.; Lombi, E. In

474

situ distribution and speciation of toxic copper, nickel, and zinc in hydrated roots of cowpea.

475

Plant Physiol. 2011, 156, 663-673.

476

(33) Zou, C. Q.; Zhang, Y. Q.; Rashid, A.; Ram, H.; Savasli, E.; Arisoy, R. Z.;

477

Ortiz-Monasterio, I.; Simunji, S.; Wang, Z. H.; Sohu, V.; Hassan, M.; Kaya, Y.; Onder, O.;

478

Lungu, O.; Mujahid, M. Y.; Joshi, A. K.; Zelenskiy, Y.; Zhang, F. S.; Cakmak, I.

479

Biofortification of wheat with zinc through zinc fertilization in seven countries. Plant Soil

480

2012, 361, 119-130.

481

(34) Ram, H.; Rashid, A.; Zhang, W.; Duarte, A. P.; Phattarakul, N.; Simunji, S.; Kalayci, M.;

482

Freitas, R.; Rerkasem, B.; Bal, R. S.; Mahmood, K.; Savasli, E.; Lungu, O.; Wang, Z. H.; de

483

Barros, V. L. N. P.; Malik, S. S.; Arisoy, R. Z.; Guo, J. X.; Sohu, V. S.; Zou, C. Q.; Cakmak, I.

484

Biofortification of wheat, rice and common bean by applying foliar zinc fertilizer along with

485

pesticides in seven countries. Plant Soil 2016, 403, 389-401.

486

(35) Cakmak, I.; Pfeiffer, W. H.; McClafferty, B. Biofortification of durum wheat with zinc

487

and iron. Cereal Chem. 2010, 87, 10-20. 23

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

488

(36) Cakmak, I.; Kalayci, M.; Kaya, Y.; Torun, A. A.; Aydin, N.; Wang, Y.; Arisoy, Z.; Erdem,

489

H.; Yazici, A.; Gokmen, O.; Ozturk, L.; Horst, W. J. Biofortification and localization of zinc

490

in wheat grain. J. Agric. Food Chem. 2010, 58, 9092-9102.

491

(37) Pfeiffer, W. H.; McClafferty, B. HarvestPlus: Breeding crops for better nutrition. Crop

492

Sci. 2007, 47, 88-105.

493

(38) Yu, M.; Yao, J.; Liang, J.; Zeng, Z.; Cui, B.; Zhao, X.; Sun, C.; Wang, Y.; Liu, G.; Cui, H.

494

Development of functionalized abamectin poly(lactic acid) nanoparticles with regulatable

495

adhesion to enhance foliar retention. RSC Adv. 2017, 7, 11271-11280.

496

(39) Ruiz, J. M.; Romero, L., Commercial yield and quality of fruits of cucumber plants

497

cultivated under greenhouse conditions: response to increases in nitrogen fertilization. J.

498

Agric. Food Chem. 1998, 46, 4171-4173.

499

(40) He, L.; Qy, W.; Rengel, Z.; Zhao, P. Zinc fertilization alters flour protein composition of

500

winter wheat genotypes varying in gluten content. Plant Soil Environ. 2016, 61, 195-200.

501

(41) Stepien, A.; Wojtkowiak, K. Effect of foliar application of Cu, Zn, and Mn on yield and

502

quality indicators of winter wheat grain. Chil. J. Agric. Res. 2016, 76, 219-226.

503

(42) Zhang, Y.; Zhang, Y.; Liu, N.; Su, D.; Xue, Q.; Stewart, B. A.; Wang, Z. Effect of

504

source-sink manipulation on accumulation of micronutrients and protein in wheat grains. J.

505

Plant Nutr. Soil Sci. 2012, 175, 622-629.

506

(43) Li, M.; Wang, S. X.; Tian, X. H.; Zhao, J.; Li, H.; Guo, C.; Chen, Y.; Zhao, A. Zn

507

distribution and bioavailability in whole grain and grain fractions of winter wheat as affected

508

by applications of soil N and foliar Zn combined with N or P. J. Cereal Sci. 2015, 61, 26-32.

24

ACS Paragon Plus Environment

Page 24 of 41

Page 25 of 41

Journal of Agricultural and Food Chemistry

509

(44) Amiri, R.; Bahraminejad, S.; Sasani, S.; Jalali-Honarmand, S.; Fakhri, R. Bread wheat

510

genetic variation for grain’s protein, iron and zinc concentrations as uptake by their genetic

511

ability. Eur. J. Agron. 2015, 67, 20-26.

512

(45) Borg, S.; Brinch-Pedersen, H.; Tauris, B.; Holm, P. B. Iron transport, deposition and

513

bioavailability in the wheat and barley grain. Plant Soil 2009, 325, 15-24.

514

(46) De Brier, N.; Gomand, S. V.; Donner, E.; Paterson, D.; Delcour, J. A.; Lombi, E.;

515

Smolders, E. Distribution of minerals in wheat grains (Triticum aestivum L.) and in roller

516

milling fractions affected by pearling. J. Agric. Food Chem. 2015, 63, 1276-1285.

517

(47) Eeckhout, W.; De Paepe, M. Total phosphorus, phytate-phosphorus and phytase activity

518

in plant feedstuffs. Anim. Feed Sci. Technol. 1994, 47, 19-29.

519

(48) Welch, R. M.; Graham, R. D. A new paradigm for world agriculture: Meeting human

520

needs. Field Crops Res. 1999, 60, 1-10.

521

(49) Lv, J.; Zhang, S.; Luo, L.; Zhang, J.; Yang, K.; Christie, P. Accumulation, speciation and

522

uptake pathway of ZnO nanoparticles in maize. Environ. Sci.: Nano 2015, 2, 68-77.

523

(50) Zhao, L. J.; Peralta-Videa, J. R.; Ren, M.; Varela-Ramirez, A.; Li, C.; Hernandez-Viezcas,

524

J. A.; Aguilera, R. J.; Gardea-Torresdey, J. L. Transport of Zn in a sandy loam soil treated with

525

ZnO NPs and uptake by corn plants: Electron microprobe and confocal microscopy studies.

526

Chem. Eng. J. 2012, 184, 1-8.

527

(51) Cakmak, I.; Kutman, U. B. Agronomic biofortifcation of cereals with zinc: a review. Eur.

528

J. Soil Sci. 2017.

529

(52) Hernandez-Viezcas, J. A.; Castillo-Michel, H.; Andrews, J. C.; Cotte, M.; Rico, C.;

530

Peralta-Videa, J. R.; Ge, Y.; Priester, J. H.; Holden, P. A.; Gardea-Torresdey, J. L. In Situ 25

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

531

synchrotron X-ray fluorescence mapping and speciation of CeO2 and ZnO nanoparticles in

532

soil cultivated soybean (Glycine max). ACS Nano 2013, 7, 1415-1423.

533

(53) Hatzack, F.; Johansen, K. S.; Rasmussen, S. K. Nutritionally relevant parameters in

534

low-phytate barley (Hordeum vulgare L.) grain mutants. J. Agric. Food Chem. 2000, 48,

535

6074-6080.

536

(54) Persson, D. P.; Hansen, T. H.; Laursen, K. H.; Schjoerring, J. K.; Husted, S.

537

Simultaneous iron, zinc, sulfur and phosphorus speciation analysis of barley grain tissues

538

using SEC-ICP-MS and IP-ICP-MS. Metallomics 2009, 1, 418-26.

539 540

FIGURE CAPTIONS

541

Figure 1. (A) A transmission electron microscopy (TEM) image of the ZnO NPs. (B)

542

Hydrodynamic size distribution of the ZnO NPs in deionized water using dynamic light

543

scattering (DLS) analysis.

544

Figure 2. A light micrograph of a cross-section of a wheat grain (as shown in Figure 3).

545

Figure 3. Distribution of Zn within transverse sections of wheat grain in Year 2 from the

546

control (CK), foliar ZnO NPs (FZnO), and Foliar ZnSO4 (FZn).

547

Figure 4. (A) Normalized Zn K-edge XANES spectra of standard compounds. (B)

548

Normalized Zn K-edge XANES spectra of wheat grains from the three treatments, being CK,

549

FZn, FZnO. (C) The comparisons of Zn K-edge XANES spectra for the grains of FZnO with

550

the Zn-phosphate (solid, Zn3(PO4)2). The vertical dotted lines in (A) and (B) correspond to

551

9.667, 9.669, and 9.671 keV, being the white-line peaks for Zn associated with P (9.667 keV),

552

Zn associated with carboxyl groups or free Zn2+ (9.669 keV), and ZnO (9.671 keV). 26

ACS Paragon Plus Environment

Page 26 of 41

Page 27 of 41

Journal of Agricultural and Food Chemistry

553 554

TABLES

555

Table 1. Basic Physical and Chemical Properties of the soil from the field sitea

556 557

Properties Value pH (Soil:water 1:2.5) 8.31 ± 0.38 Calcium carbonate (%) 9.75 ± 0.15 Organic C (%) 1.55 ± 0.08 Sand (%) 27 ± 0.7 Silt (%) 39 ± 0.9 Clay (%) 34 ± 0.0 18.6 ± 0.10 Cation exchange capacity (cmolc/kg) DTPA-Zn (mg/kg) 0.49 ± 0.14 Total Zn (mg/kg) 63.6 ± 8.12 Total N (mg/kg) 1040 ± 61.23 Available P (mg/kg) 18.8 ± 7.16 Available K (mg/kg) 154.5 ± 14.17 a Data are means of four replicates ± standard deviation. Available P was extracted by 0.5 M NaHCO3, and available K was extracted using 1 M NH4AC.

27

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

558 559

Table 2. Effects of ZnO NPs and ZnSO4 on Grain Yield and Zn Concentrationa Year 1

Year 2

treatment

560 561

grain yield Zn grain yield Zn (kg/ha) (mg/kg) (kg/ha) (mg/kg) CK 7881 ± 216 a 18.4 ± 0.13 c 5412 ± 279 a 23.6 ± 0.83 c FZnO 7750 ± 437 a 26.5 ± 0.60 a 5062 ± 288 a 34.6 ± 1.40 a FZn 7820 ± 692 a 21.1 ± 0.05 b 5157 ± 485 a 29.5 ± 0.30 b a Data are means of four replicates ± standard deviation. Different letters within same column indicate significant difference at 0.05 level.

28

ACS Paragon Plus Environment

Page 28 of 41

Page 29 of 41

Journal of Agricultural and Food Chemistry

562 563

564 565 566

Table 3. Effects of ZnO NPs and ZnSO4 on Soluble Sugars and Starcha Year 1 Year 2 treatment soluble sugars starch soluble sugars starch (%) (%) (%) (%) CK 27.45 ± 2.13 a 51.45 ± 0.43 a 24.00 ± 3.12 a 50.27 ± 0.69 a FZnO 28.17 ± 3.15 a 52.33 ± 0.13 a 24.46 ± 1.44 a 48.66 ± 0.75 a FZn 26.98 ± 2.46 a 52.02 ± 0.99 a 24.08 ± 5.47 a 48.64 ± 2.40 a a Data are means of four replicates ± standard deviation. Different letters within same column indicate significant difference at 0.05 level.

29

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

567

Table 4. Effects of ZnO NPs and ZnSO4 on Crude Protein and Its Fraction (%)a Year 1 Year 2 CK FZnO FZn CK FZnO FZn crude protein 11.33 ± 0.23 a 11.49 ± 0.07 a 11.51 ± 0.48 a 11.96 ± 0.30 a 12.03 ± 0.25 a 12.22 ± 0.46 a albumin 2.27 ± 0.09 a 2.32 ± 0.10 a 2.33 ± 0.05 a 2.39 ± 0.06 a 2.41 ± 0.05 a 2.44 ± 0.09 a globulin 0.91 ± 0.06 a 0.93 ± 0.07 a 0.96 ± 0.03 a 0.96 ± 0.02 a 0.96 ± 0.02 a 0.98 ± 0.04 a prolamin 3.39 ± 0.03 a 3.45 ± 0.12 a 3.43 ± 0.04 a 3.59 ± 0.09 a 3.61 ± 0.08 a 3.67 ± 0.14 a glutelin 2.83 ± 0.06 a 2.88 ± 0.05 a 2.84 ± 0.02 a 2.99 ± 0.07 a 3.01 ± 0.66 a 3.05 ± 0.12 a a Data are means of four replicates ± standard deviation. Different letters within same row indicate significant difference at 0.05 level. Trait

568 569

30

ACS Paragon Plus Environment

Page 30 of 41

Page 31 of 41

Journal of Agricultural and Food Chemistry

570

FIGURE GRAPHICS

571 572

Figure 1. (A) A transmission electron microscopy (TEM) image of the ZnO NPs. (B)

573

Hydrodynamic size distribution of the ZnO NPs in deionized water using dynamic light

574

scattering (DLS) analysis.

575

31

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

576 577

Figure 2. A light micrograph of a cross-section of a wheat grain (as shown in Figure 3).

32

ACS Paragon Plus Environment

Page 32 of 41

Page 33 of 41

Journal of Agricultural and Food Chemistry

578 579

Figure 3. Distribution of Zn within transverse sections of wheat grain in Year 2 from the

580

control (CK), foliar ZnO NPs (FZnO), and Foliar ZnSO4 (FZn).

33

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

581 582

Figure 4. (A) Normalized Zn K-edge XANES spectra of standard compounds. (B)

583

Normalized Zn K-edge XANES spectra of wheat grains from the three treatments, being CK,

584

FZn, FZnO. (C) The comparisons of Zn K-edge XANES spectra for the grains of FZnO with

585

the Zn-phosphate (solid, Zn3(PO4)2). The vertical dotted lines in (A) and (B) correspond to

586

9.667, 9.669, and 9.671 keV, being the white-line peaks for Zn associated with P (9.667 keV),

587

Zn associated with carboxyl groups or free Zn2+ (9.669 keV), and ZnO (9.671 keV).

588

34

ACS Paragon Plus Environment

Page 34 of 41

Page 35 of 41

Journal of Agricultural and Food Chemistry

589

TOC

590 591

For Table of Contents Only

35

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Figure 1. (A) A transmission electron microscopy (TEM) image of the ZnO NPs. 59x51mm (300 x 300 DPI)

ACS Paragon Plus Environment

Page 36 of 41

Page 37 of 41

Journal of Agricultural and Food Chemistry

Figure 1. (B) Hydrodynamic size distribution of the ZnO NPs in deionized water using dynamic light scattering (DLS) analysis. 90x60mm (300 x 300 DPI)

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Figure 2. A light micrograph of a cross-section of a wheat grain (as shown in Figure 3). 80x60mm (300 x 300 DPI)

ACS Paragon Plus Environment

Page 38 of 41

Page 39 of 41

Journal of Agricultural and Food Chemistry

Figure 3. Representative Zn µ-XRF mapping of the grain transverse sections in Year 2 from the control (CK), foliar ZnO NPs (FZnO), and Foliar ZnSO4 (FZn). 80x80mm (600 x 600 DPI)

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Figure 4. (A) Normalized Zn K-edge XANES spectra of standard compounds. (B) Normalized Zn K-edge XANES spectra of wheat grains from the three treatments, being CK, FZn, FZnO. (C) The comparisons of Zn K-edge XANES spectra for the grains of FZnO with the Zn-phosphate (solid, Zn3(PO4)2). The vertical dotted lines in (A) and (B) correspond to 9.667, 9.669, and 9.671 keV, being the white-line peaks for Zn associated with P (9.667 keV), Zn associated with carboxyl groups or free Zn2+ (9.669 keV), and ZnO (9.671 keV). 90x98mm (600 x 600 DPI)

ACS Paragon Plus Environment

Page 40 of 41

Page 41 of 41

Journal of Agricultural and Food Chemistry

For Table of Contents Only 47x26mm (600 x 600 DPI)

ACS Paragon Plus Environment