Titanium Dioxide in Food Products: Quantitative Analysis using ICP

Dec 4, 2018 - These values obtained using inductively coupled plasma-mass spectrometry (ICP-MS) were considered as the reference and were compared ...
5 downloads 0 Views 812KB Size
Subscriber access provided by TULANE UNIVERSITY

New Analytical Methods

Titanium Dioxide in Food Products: Quantitative Analysis using ICP-MS and Raman Spectroscopy Jin-Hee Lim, Dongryeoul Bae, and Andrew Fong J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.8b06571 • Publication Date (Web): 04 Dec 2018 Downloaded from http://pubs.acs.org on December 5, 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 35

Journal of Agricultural and Food Chemistry

1

Titanium Dioxide in Food Products: Quantitative Analysis using ICP-MS and Raman

2

Spectroscopy

3

Jin-Hee Lim*, Dongryeoul Bae, and Andrew Fong

4

Office of Regulatory Affairs, Arkansas Laboratory, U.S. Food and Drug Administration, 3900

5

NCTR Road, Jefferson, Arkansas 72079, United States

6 7

*Corresponding author

8

Tel: +1-870-543-4660

9

Fax: +1-870-543-4021

10

Email: [email protected] or [email protected]

11 12 13 14 15 16 17

1

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

18

Abstract

19

Titanium dioxide (TiO2) is commonly used as a color additive in food products. In this study, a

20

total of eleven food products such as coffee cream, yogurt snack, hard candy and chewy candy

21

that are widely consumed by adults or children were investigated. For characterization of particle

22

size, size distribution, crystallinity and concentration of TiO2, particles were first extracted using

23

an acid digestion method from food and various analytical techniques were applied. All products

24

investigated in this study contained nanosized TiO2 particles (21.3-53.7%) in the anatase phase.

25

The particle size of TiO2 was in a range of 26.9-463.2 nm. The concentration of TiO2 in the

26

products ranged from 0.015% (150 ppm) to 0.462% (4620 ppm). These values obtained using

27

inductively coupled plasma-mass spectrometry (ICP-MS) were considered as the reference and

28

were compared with Raman results to evaluate the feasibility of using the Raman method to

29

quantitate TiO2 in food products. The Raman method developed in this study proved to

30

effectively analyze anatase TiO2 in food products at levels of several hundred ppm or greater.

31

Limitations of using the Raman method as a quick screening tool for determination of TiO2 are

32

also discussed.

33

Keywords: Titanium dioxide, nanoparticles, color additives, ICP-MS, Raman spectroscopy

34 35 36 37

2

ACS Paragon Plus Environment

Page 2 of 35

Page 3 of 35

Journal of Agricultural and Food Chemistry

38

Introduction

39

Titanium dioxide (TiO2) is widely used in versatile applications to improve the quality and

40

palatability of consumer products such as food, personal care products, cosmetics, paints and

41

coatings.1-3 With the wide use of TiO2 in various industries, nanosized TiO2 has raised safety

42

questions regarding uncontrolled release and potential adverse impact of TiO2 nanoparticles

43

(NPs) to the environment and human health.1, 4, 5 The first step in most risk assessment is an

44

identification and characterization of nanomaterials. Understanding the physicochemical

45

properties of TiO2 such as particle size, size distribution, shape, crystal structure, ionization

46

conditions, coating materials, aggregation status, and particle concentration is an important factor

47

to be considered as part of risk assessment.1 Although many studies have been conducted for

48

developing analytical methods in the food industry, a major challenge in conducting research on

49

analytical method development involve techniques to efficiently and effectively identify

50

nanoparticles present in complex matrices and to determine the physicochemical properties of

51

nanomaterials.6-9

52

Many advanced techniques, including electron microscopy, spectroscopy, mass spectroscopy, X-

53

ray diffraction (XRD), x-ray fluorescence (XRF), and light scattering, have been applied to

54

characterize physicochemical properties of TiO2 in consumer products. Among these techniques,

55

size characterization methods have been extensively developed. In recent years, field flow

56

fractionation, capillary electrophoresis, and single particle inductively coupled plasma mass

57

spectrometry (spICP-MS) which can separate nanomaterials and determine particle size

58

simultaneously have emerged as viable methods.10-14 However, using an electron microscope

59

with energy dispersive X-ray spectroscopy (EDS) is still the most widely applied method for 3

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

60

determining the size, morphology, and aggregation status analysis of TiO2.13-16 In some cases,

61

the selected area electron diffraction (SAED) patterns generated by transmission electron

62

microscope (TEM) were used to identify crystalline information.17, 18 For qualitative and

63

quantitative trace element analysis, inductively coupled plasma-mass spectrometry (ICP-MS) has

64

been commonly used.5, 14 The quality of ICP-MS data for TiO2 analysis is highly dependent on

65

sample preparation. Digesting the sample to a clear solution is essential for accurate analysis of

66

materials using ICP-MS. Samples such as TiO2, SiO2 or carbon nanotubes, which are very stable

67

in acids, require additional efforts for complete digestion. TiO2 is stable in nitric acid (HNO3),

68

and slowly ionized in hydrofluoric (HF) acid.19, 20 Using a mixture of concentrated HNO3 and HF

69

for sample digestion, more accurate and reliable results were obtained.11, 20-23 However, HF is an

70

extremely dangerous chemical and requires diligence and utmost caution when used.

71

Due to difficulties of ionizing TiO2 in ICP-MS analysis, researchers developed new approaches

72

for TiO2 quantitation.23-25 One of the more recently developed methods for quantitation of food

73

additives or toxic materials in food involved Raman spectroscopic methods.24-29 There are

74

several research articles describing quantitative analysis of food products using Raman.26, 30-32

75

Tan et al.32 described a single-drop Raman imaging technique for the analysis of trace

76

contaminants in milk and Weng et al.31 reported quantitative analysis of ediphenphos residue in

77

rice. Another group24, 25, 33 reported the quantitation of TiO2 in table sugar using Raman

78

spectroscopy and also developed the flavonoid-assisted microextraction method for TiO2

79

detection. The published methods showed a simple and rapid quantitative Raman method with

80

standard TiO2 powders; however, those methods have limitations when applied to complex food

81

matrices containing multiple organic and inorganic compounds. In addition, more studies are 4

ACS Paragon Plus Environment

Page 4 of 35

Page 5 of 35

Journal of Agricultural and Food Chemistry

82

necessary to develop extraction methods to reduce or eliminate strong fluorescence effects

83

caused by various food ingredients or to improve recovery.

84

The aim of this work was to characterize TiO2 nanoparticles in consumer products such as coffee

85

cream, yogurt snack, hard candy, chewy candy which are widely consumed by adults or children,

86

and to evaluate the feasibility of Raman method to be used as a quick and simple technique for

87

the quantitative determination of TiO2 in complex matrices. The TiO2 concentration determined

88

by ICP-MS was used as a reference value to evaluate the accuracy of the Raman technique. The

89

limitations of Raman spectroscopy associated with quantitation of total TiO2 in commercial

90

products are presented.

91

Materials and Methods

92

Titanium - Ti (1000 and 10,000 mg/kg) and Scandium - Sc (1000 mg/kg) single-element ICP-

93

MS standard solutions were acquired from Ultra Scientific (Metuchen, NJ), Ricca Chemical Co.

94

(Arlington, TX), and Spex CertiPrep Group (Metuchen, NJ). TiO2 powders were purchased from

95

the national institute of standards and technology (NIST 1898; Gaithersburg, MD), US Research

96

Nanomaterials, Inc. (30-50 nm, Rutile, Houston, TX), nanoComposix Inc. (25 nm, 80%

97

anatase/Rutile, San Diego, CA), Pronto Foods (Food & Pharmaceutical grade; Chicago, IL), and

98

MakingCosmetics Inc. (Snoqualmie, WA). Nitric acid (HNO3, Optima 67-70%), hydrofluoric

99

acid (HF, Optima 41-51%), hydrogen peroxide (H2O2, Optima 30-32%) ethanol (C2H5OH,

100

denatured), and acetone [(CH3)2CO, ACS grade] were purchased from Fisher Scientific (Houston,

101

TX). Aluminum oxide (Al2O3, >98%) was obtained from Sigma Aldrich (St. Louis, MO). Silicon

102

oxide (SiO2, 99.9%, 20-60 nm) was purchased from SkySpring Nanomaterials, Inc. (Houston,

103

TX). Type I ultra-pure water (18MΩ-cm) was available through a Direct-Q 3UV water 5

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

104

purification system (EMD Millipore, Billerica, MA). The commercial products that claimed to

105

contain TiO2, color additives, E171 white coloring, or artificial color were randomly obtained

106

from various retailers, where E numbers are codes for specific substances used as food additives

107

in Europe.34, 35 A total of eleven products, including coffee cream, cookie, yogurt snack, hard

108

candy and chewy candy were tested and reported in this study. Each product was given a unique

109

identification name such as RS01-RS11. Product information is listed in Table 1.

110

TiO2 Particle Extraction from Food Products

111

Sample products selected in this study contain various food ingredients or organic compounds.

112

To remove the complex matrices, TiO2 containing products were digested in HNO3.

113

Approximately 100-200 mg of each sample and 2 mL of nitric acid were heated at 180 ˚C for 3

114

min using a Mars 6 microwave digestion system (CEM, Matthews, NC). Some samples such as

115

candy, which has a very low concentration of TiO2 and contain various food color additives,

116

needed an additional pre-extraction procedure. Approximately 1 g of candy samples was first

117

dissolved in a 5 mL of mixture solution containing H2O2/HNO3 (10:0.1, v/v) at 80 ˚C. After the

118

solid food was dissolved, the samples were centrifuged at 7000 × g for 10 min and the precipitate

119

only was acid digested in 2 mL of nitric acid at 180 ˚C for 3 min. Digested solutions were then

120

transferred into 15 mL tubes and centrifuged at 7000 × g for 10 min. After centrifugation,

121

extracted particles were rinsed with ultra-pure water and acetone three times. For further analysis,

122

the extracted particles were dispersed in ethanol and stored at room temperature.

123

X-Ray Diffraction (XRD)

6

ACS Paragon Plus Environment

Page 6 of 35

Page 7 of 35

Journal of Agricultural and Food Chemistry

124

The crystalline structure of TiO2 was characterized using an AXS XRD D2 Phaser (Bruker,

125

Madison, WI) operated at 30 kV and 10 mA at 24 ˚C. Particles dispersed in ethanol were placed

126

onto the zero diffraction silicon sample holder purchased from MTI Corp. (Richmond, CA).

127

Dried samples were loaded into the instrument and XRD patterns were collected from 20-80˚ (2θ)

128

using a Lynxzeye decector (Bruker) and Cu Kα (λ=1.541 Å) radiation. The data was analyzed

129

using EVA 4.6 software.

130

Transmission Electron Microscopy (TEM)

131

A 2100 TEM (JEOL, Peabody, MA) operated at acceleration voltage of 200 kV was used for

132

particle size characterization. Elemental analysis data was collected using an Oxford X-Max 80T

133

EDS system. The isolated TiO2 particles were dispersed in ethanol and sonicated using ultrasonic

134

bath for 10 min. A small amount (5-10 µL) of sample was placed on a carbon coated Cu grid

135

(300-mesh) and dried overnight. The TiO2 particle size was statistically determined using ImageJ

136

(NIH, Bethesda, MD).

137

Inductively Coupled Plasma-Mass Spectrometry (ICP-MS)

138

To determine Ti concentration, sample products were first digested in an acid matrix using a

139

MARS-Xpress microwave digester (CEM) (maximum power: 1600 W). Approximately 100 mg

140

of sample products, 3 mL of HNO3, and 1 mL of HF were transferred into a digestion vessel.

141

Samples were digested at 210 ˚C for 20 min. After microwave digestion, the sample solutions

142

were diluted to 25 mL with ultra-pure water. A second dilution step was performed by diluting

143

0.1-1 mL of diluent to 50 mL with ultra-pure water and internal standard (Sc) added. The

144

samples were analyzed using an 8800 ICP-QQQ with a PFA inert kit and nebulizer (Agilent 7

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

145

Technologies, Santa Clara, CA). The concentrations of Ti were determined in single mode (m/z

146

47) with Helium (He) collision cell.23 Initial and continuing calibration verification standards,

147

reagent and sample blanks were prepared and analyzed along with the samples. A weight

148

fraction of Ti was calculated from the molecular weight of TiO2 (Ti=60%) and was used to

149

determine percent (%) concentration of TiO2 in food products. All samples for ICP-MS were

150

analyzed in triplicate.

151

Raman Spectroscopy

152

Raman scattering measurements were performed using a LabRam HR Raman spectrometer

153

equipped with a 633 nm excitation laser and a 10X objective (Horiba Scientific, Edison, NJ). The

154

spatial resolution and laser spot diameter were approximately 1.5 µm and 3.0 µm, respectively.

155

The Raman spectra were obtained with a 100 µm slit aperture with a 5 s acquisition time.

156

LabSpec 6.4 software was used for Raman data acquisition and analysis. The TiO2 calibration

157

curve was developed with six independent TiO2 working standards with 0.07-2.3wt%. The

158

calibration standard powders were prepared by mixing anatase TiO2 particles (food and

159

pharmaceutical grade) with Al2O3. In the case of food samples, particles were extracted by acid

160

digestion described previously. Dried particles were mixed with Al2O3, where the amount of

161

Al2O3 was dependent on the original amount of each sample digested (100-200mg). In the case

162

of RS06, multiple samples were digested to prepare one Raman sample due to low TiO2

163

concentration and the extracted TiO2 was concentrated almost 20-fold while mixed with Al2O3.

164

The mass of extracted samples and Al2O3 were recorded. Well mixed standards or samples were

165

placed onto a glass slide and pressed with another slide in order to make a flat surface. A flat

166

surface facilitated focusing and moving the stage quickly. To improve the accuracy of 8

ACS Paragon Plus Environment

Page 8 of 35

Page 9 of 35

Journal of Agricultural and Food Chemistry

167

quantitative analysis, more than fifteen discrete locations in each sample were selected under the

168

Raman microscope by controlling x-y axis and scanned in the range of 50-800 cm-1. All

169

experiments were performed in triplicate with independent samples and average concentration

170

reported.

171

Results and Discussion

172

A total eleven food products were selected and procured for this study. A list of products with

173

sample identification number, product type, and TiO2 label information are provided in Table 1.

174

Ten of the eleven products investigated clearly listed the presence of TiO2 as ‘Titanium Dioxide’

175

with color, color additives, or E171. However, the RS03 product label just indicated the presence

176

of color additive as ‘Color added’. The color of the eleven products was diverse and many other

177

color additives were listed along with TiO2 on their ingredient list.

178

Crystallinity, Shape, Particle Size and Size Distribution Analysis

179

To isolate TiO2 particles from the complex matrices, the acid digestion method was adopted in

180

this study. The TiO2 recovery after the extraction procedures was tested before the method was

181

applied to sample products. Between 91.4-96.3% of TiO2 spiked in chewy candy, sucrose, and

182

water samples were extracted after the acid digestion and centrifugation procedures (n=6). This

183

test confirmed that the extraction efficiency was higher than 90%. In addition, the pure particles

184

and the extracted particles were characterized to prove that the method did not alter the size,

185

morphology and crystallinity of TiO2 particles. The XRD patterns of TiO2 before and after

186

extraction presented only anatase. In this study, it was difficult to demonstrate statistically how

187

much the acid effect on particle size and morphology of TiO2 because of the broad size 9

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

188

distribution of TiO2 and the characteristic of TiO2 easily agglomerate/aggregate in water.

189

However, the preliminary results proved that this extraction method can be applied to

190

characterize size and concentration of TiO2 in food products using various analytical instruments

191

below.

192

To isolate TiO2 particles from the complex matrices, all food products were acid digested leaving

193

TiO2 as an insoluble precipitate. Following digestion, the white TiO2 particles were collected

194

after centrifugation. The crystallinity, shape, particles size and size distribution were

195

characterized using TEM and XRD. This method allowed detection of very low amount of

196

particles in products such as in RS06. The limit of sensitivity for detecting the other phases of

197

TiO2 was evaluated with mixture of anatase and rutile TiO2 powders. The XRD results proved

198

that the instrument was sufficient to detect approximately 1% rutile in 99% anatase TiO2. As

199

shown in Figure 1, TiO2 particles extracted from the food products (RS01-RS11) were in the

200

anatase phase. No other types of TiO2 structures such as rutile or brookite were detected. The

201

peak positions were consistent with the standard diffraction pattern of anatase TiO2 (JCPDS no.

202

21-1272).22 Diffraction peaks were found at 2θ = 25.3°, 36.9°, 37.8°, 38.5°, and 48.1°, which can

203

be indexed to the (101), (103), (004), (112), and (200) planes. Some impurities were found at

204

28.7° in RS07, but the peak did not correspond to any peaks of rutile phase at 2θ = 27.5°, 36.3°,

205

41.3°, 54.4°, 62.8° (JCPDS no. 21-1276). Figure 2 showed TEM images and size distribution

206

histograms. The extracted nanoparticles were mostly spherical in shape, but some particles were

207

rod-shaped. In addition, as expected, many particles were aggregated and size ranged from

208

several hundred nanometers to several micrometers. The size of individual TiO2 particles was

209

calculated using ImageJ software and more than 350 particles of each sample were measured. As

210

shown in Table 1 and Figure 2, the particles had a broad size distribution, between 26.9 and 10

ACS Paragon Plus Environment

Page 10 of 35

Page 11 of 35

Journal of Agricultural and Food Chemistry

211

463.2 nm. The smallest particle sizes of TiO2 found in products were between 26.9 and 40.3 nm

212

and all products contained particles that were less than 100 nm. The mean particle size of each

213

product was in the range of 103.5-147.8 nm. The size distribution histogram of each product was

214

generated to examine the ratio of nanoparticles in total TiO2 detected in the food products

215

(Figure 2). In this study, 21.3-53.7% of TiO2 were found to be nanosized particles and the values

216

varied within products without any relationship to product type. A large number of nanosized

217

TiO2 particles were found in RS03 (49.8%), RS04 (53.7%) and RS09 (50.4%). Comparison of

218

TiO2 particles found in the foods and food grade TiO2 powders proved that size distribution,

219

shape and aggregation/agglomeration of TiO2 were very similar (data not presented).

220

ICP-MS Analysis

221

ICP-MS was chosen as a determinative technique for the quantitative analysis of the food

222

products studied for TiO2. The ICP-MS instrument was calibrated for Ti with seven calibration

223

solutions ranging in concentration from 10 to 500 µg/L. The calibration resulted in a correlation

224

coefficient (r2) with excellent linearity (≥ 0.9999). For the system suitability test, seven

225

consecutive injections of a standard that contains mid-level (0.2 mg/L) concentration were

226

performed.36 The average concentration of seven consecutive injections and relative standard

227

deviation (RSD) were 197.5±1.4 (98.8% recovery) and 0.7%, respectively. Method detection

228

limit (MDL) was calculated by multiplying the student's t value (3.143) for the seven replicates

229

(n=7) by the standard deviation of the calibration standard at the lowest analyte concentration

230

(0.010 mg/L of Ti).23, 36 Limit of quantitation (LOQ) was defined as 10 times the standard

231

deviation. MDL and LOQ for ICP-MS analysis were 0.001 mg/L and 0.004 mg/L, respectively.

232

Continuing calibration verification (CCV), initial calibration verification (ICV) and spiked 11

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

233

sample recovery (acid digested) were also determined in the validation process. The recovery

234

values of CCV and ICV were in the range of 100-107%. The spiked sample recovery was

235

102.6%. The concentration of Ti in reagent blank and sample blank was examined at least once a

236

batch and the determined concentration was always much lower than MDL. All test results for

237

method validation showed good accuracy and precision, within ±10% of nominal values and less

238

than 2.0% of RSD.

239

After method validation, eleven products containing anatase TiO2 were characterized by ICP-

240

MS. The concentration of TiO2 (%) in each product is shown in Table 1. The range of TiO2

241

concentrations in the products was between 0.015% and 0.462% (150-4620 mg/kg). As

242

mentioned earlier, some of the products such as chewy candy showed multiple colors, which

243

means various color additives were used to present a specific color. However, the ICP-MS

244

results showed that the amount of TiO2 present in each sample with different colors was very

245

close and that the TiO2 was homogeneously distributed regardless of sample product color.

246

The U.S. Food and Drug Administration approved the use of TiO2 in 1966 with an allowed limit

247

of TiO2 in food at 1% of the overall food weight (US FDA 21CFR73.575).37, 38 The

248

concentrations of TiO2 used as color additives in these products were much lower than the 1%

249

limit of TiO2.

250

Raman Analysis

251

We have developed a quantitation method for the determination of TiO2 in commercial food

252

products using a Raman spectroscopy. Anatase TiO2 showed a strong peak at 143 cm-1 followed

253

by low intensity peaks located at 196, 395, 518 and 638 cm-1, which can be assigned as Eg, Eg,

254

B1g, A1g+B1g, Eg modes, respectively.39 For quantitative analysis, six working standard powders 12

ACS Paragon Plus Environment

Page 12 of 35

Page 13 of 35

Journal of Agricultural and Food Chemistry

255

ranging from 0.05-2.36% TiO2 (700 mg/kg to 23600 mg/kg) were prepared and Raman signals

256

for each standard were recorded. A calibration curve was constructed from a series of standards

257

(Figure 3), where the x-axis is the known concentration (%) and the y-axis is the intensity of

258

peaks at 143 cm-1. Values for slope (m) and the y-intercept (b) were determined using Origin Pro

259

software. The Raman signal at 143 cm-1 increased in proportion to the particle concentration and

260

the calibration curve showed a good linear correlation (r2=0.9982). The calibration curve was

261

verified by measuring twelve independent standard powders with various concentrations (0.3-2.0%

262

TiO2). The percent recovery values (%RV) for twelve calibration verification samples was

263

between 85.4 and 108.8%, and average recovery was 96.1±7.1%, exhibiting good reproducibility

264

by this quantitative Raman determinative method. In addition, to evaluate the quality of Raman

265

working standard, three independent samples with approximately 1% TiO2 (10000 mg/Kg) were

266

also analyzed by ICP-MS (Table 2). The recoveries for ICP-MS and Raman analyses were

267

calculated as follows:

268

%RV1= ([TiO2]ICP-MS / [TiO2]known value) × 100

269

%RV2= ([TiO2]Raman / [TiO2]ICP-MS) × 100

270

where [TiO2]ICP-MS are the TiO2 concentration determined by ICP-MS, [TiO2]Raman are the TiO2

271

concentration determined by Raman, and [TiO2]known value is the theoretical values. Correlation

272

between the ICP-MS and Raman techniques was determined by calculating the difference value

273

(DV). %DV were defined as

274

%DV= ([TiO2]Raman - [TiO2]ICP-MS) / (([TiO2]Raman + [TiO2]ICP-MS)/2) × 100

13

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

275

The mean %RV for ICP-MS and Raman ranged from 91.9-106.3% and the %DV for the

276

standard samples between ICP-MS and Raman methods were found to be less than 10% (Table

277

2). These results indicate that powder working standards can be applied to quantitative

278

determination of TiO2 particles using Raman.

279

To calculate MDL and LOQ for Raman analysis, seven individual measurements were carried

280

out using the lowest calibration standard (0.05%). The calculated MDL and LOQ were 0.006%

281

(60 mg/kg) and 0.02% (200 mg/kg), respectively. LOQ is the lowest concentration reportable for

282

Raman analysis, but does not imply that only products containing more than 0.02% can be

283

analyzed. In this study, samples were concentrated while the particles were isolated and mixed

284

with Al2O3 matrix. In some cases, the final TiO2 concentration in Al2O3 was 10 times higher than

285

the original concentration. For example, the original concentration of yogurt snack sample (RS06)

286

has 0.013% TiO2 (130 mg/kg) in products (lower than LOQ). However, TiO2 were detectable by

287

Raman after concentration from the extraction process. The %RV for this sample was 86.7% as

288

shown in Table 1. To test extraction efficiency, five independent spiked samples were prepared

289

and analyzed by Raman. Test results are summarized in Table 3. Recoveries of each spiked

290

sample ranged between 107.2% and 117.0%, which are higher than expected (average recovery:

291

112.9%).

292

After the Raman method validation, quantitative analyses of RS01-RS11 samples were

293

conducted and results are summarized in Table 1. For efficient TiO2 extraction, nitric acid was

294

used to digest food and other ingredients, excluding TiO2. Recovery (%RV2) results demonstrate

295

that almost all food compounds were successfully digested and extracted TiO2 particles were

296

well distributed in Al2O3. Because original concentration of TiO2 information in food products is 14

ACS Paragon Plus Environment

Page 14 of 35

Page 15 of 35

Journal of Agricultural and Food Chemistry

297

not available on label (manufacturers are not required to label the final concentration of TiO2 in

298

food products), Raman results were only compared with ICP-MS data. The %RV2 ranged from

299

86.7-116.0%. The %DV was between -14.3 and 14.8%. These data demonstrate that the Raman

300

technique was able to quantitate % concentration of TiO2 particles in food products (RS01-RS11)

301

as shown by %DV under ±20% for each concentration level analyzed. In addition, this Raman

302

technique can be utilized as an alternative method to quantitate metal oxide compounds such as

303

TiO2 in food.

304

To achieve better quantitative results using Raman spectroscopy, one should consider several

305

factors which can affect the Raman analysis: mixing with Al2O3 matrix; fluorescence effect;

306

crystallinity of TiO2; and other ingredients remaining after acid extraction. As shown in TEM

307

image (Figure 2 and Table 1), some extracted particles aggregated and particle size varied from

308

nanometer to micrometer. Particle aggregation in the matrix can cause signal variation. For a

309

successful quantitative analysis, the particles were first milled and redispersed in Al2O3 matrix

310

after acid extraction. With the large laser spot diameter and multiple scans (n≥15) of each sample,

311

the variation also decreased. A large number of replicates ensured the reliability of the method,

312

although the process was time consuming. The Al2O3 matrix is commonly found in environment

313

and is very stable in air. Al2O3 does not interfere with Raman scattering for TiO2.

314

Various organic compounds added in commercial products can create strong fluorescence effects

315

on Raman scattering and the intense background can hide Raman peaks scattered from target

316

materials. In addition, the fluorescence background is also found when particles contain

317

amorphous TiO2 or have defects in the crystal structure (oxygen vacancies in the nanocrystal

318

structure).40, 41 In this study, some samples such as RS07, RS08, RS10, and RS11 showed a 15

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

319

strong fluorescence background. RS07 samples had more than 4000 background intensity in the

320

first scan. With strong florescence effects, the peak intensity at 143 cm-1 was not correlated with

321

the calibration curve. To decrease background intensity, the photobleaching method, which is

322

based on constant sample irradiation for a long period of time using a same light source, was

323

attempted.42 After multiple scans at the same position, background counts were reduced to

324

around 1000 counts. However, the peak height (h) at 143 cm-1 for each scan was not influenced

325

by the fluorescence background, but no significant changes were found in each scan. For those

326

samples showing strong fluorescence background, samples were irradiated at least three times

327

before acquiring a spectrum. With calculation of the peak height at 143 cm-1, acceptable values

328

for RS07, RS08, RS10, and RS11 were obtained and summarized in Table 1.

329

SiO2 is a food additive widely used as an anti-caking agent in food. The U.S. FDA approved the

330

use of up to 2.0% SiO2 by weight of the food (U.S. FDA 21CFR172.480).43 As shown in Table 1,

331

RS02 label claimed to contain both TiO2 and SiO2. While TiO2 particles were extracted in nitric

332

acid, SiO2 were also isolated and mixed with Al2O3 matrix before Raman analysis. To evaluate

333

any effect of SiO2 on TiO2 quantitation, SiO2 nanoparticles (1.98%) were mixed with TiO2

334

(1.50%) and measured by Raman (Figure 4). A negligible fluorescence background was

335

observed at this concentration, and an average recovery value of TiO2 was 98.6%. In addition,

336

peak positions of the Al2O3 matrix and SiO2 were not overlapped with anatase TiO2. However,

337

peaks for rutile TiO2 were very close to anatase phase and the main peak of anatase at 143 cm-1

338

was overlapped with rutile phase.

339

Anatase and rutile phase of TiO2 are commonly used in food and cosmetic products,

340

respectively.22, 44 In cases of mixtures of anatase and rutile TiO2 in samples, the rutile peak 16

ACS Paragon Plus Environment

Page 16 of 35

Page 17 of 35

Journal of Agricultural and Food Chemistry

341

interfered with the peak intensity of anatase TiO2 at 143 cm-1 resulting in poor recovery. When

342

TiO2 containing anatase and rutile (80:20, nanoComposix) was measured by Raman, the average

343

recovery of anatase with the current calibration curve was 20.1% (n=3). If the TiO2 is extracted

344

from the sample and crystallographic data indicate the presence of both anatase and rutile TiO2,

345

Raman quantitative methods would not be appropriate. Although this study did not include any

346

products containing both anatase and rutile forms of TiO2, consideration of the crystalline

347

structures is important when Raman quantitation method is applied.

348

Concentrations of TiO2 particles were accurately quantitated using the Raman method developed

349

in the current study. By comparing the Raman results with ICP-MS, the accuracy of the method

350

was evaluated. Our results demonstrated that the Raman technique is feasible for both qualitative

351

and quantitative analysis of TiO2 in food products. Several factors such as extraction method,

352

fluorescence effect, purity of material, crystallinity, mixing with new matrix can affect the final

353

results. A suitable extraction/precipitation method which does not alter the properties of material,

354

but reduces fluorescence effects is required to improve the accuracy of the Raman method for

355

quantitative analysis.

356

Developing new analytical methods is scientifically and academically significant. The

357

quantitative methods developed by the He group24, 25, 30 led to the conclusion that Raman

358

spectroscopy is less sensitive and difficult to apply for quantitative analysis. Their methods

359

showed higher sensitivity (2 mg/kg of detection limit for anatase TiO2) compare to our method

360

(60 mg/kg of detection limit). They also demonstrated that the existing methods are accurate and

361

can be applied to detect TiO2 in pure or simple matrix such as table sugar or spiked samples such

362

as pond water. However, the published methods were difficult to directly apply to commercial 17

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

363

products containing multiple ingredients for survey study or risk assessment. Commercial food

364

products are not as simple as the specimens used in their studies. Foods contain various organic

365

and inorganic compounds and these materials can interfere or reduce the Raman intensity of

366

TiO2. Specially, metal oxide (i.e., ZnO, SiO2, iron oxide, calcium phosphate, etc.) remaining

367

after centrifugation and organic compounds producing strong a fluorescent effect could be main

368

issues with the existing methods to quantitate TiO2 in food products, waste water (environmental

369

samples) or drug products. In contrast, our acid extraction and Raman method could minimize

370

those issues and have better accuracy when the Raman technique applied to quantitate TiO2

371

particles in complex matrices. However, it is very important to note that the accuracy of Raman

372

methods can be reduced dramatically when both anatase and rutile TiO2 exist in one sample. The

373

mixed form of TiO2 was found in commercial products in our previous studies.22, 41 Quantitating

374

mixed TiO2 in complex matrices and improving the sensitivity are still challenging.

375

For a realistic estimation of oral intake of TiO2, further investigations will be explored. It could

376

include more information on the number and types of food products containing TiO2, and the

377

concentration of TiO2 in these products. In addition, tracking the source of raw materials and

378

manufacturing processes producing food grade TiO2 powders could help the identification of

379

presence of nanomaterials in the final products.

380 381

Abbreviations Used

382

ICP-MS, inductively coupled plasma mass spectrometry; XRD, X-ray diffraction; EDS, energy

383

dispersive X-ray spectroscopy; TEM, transmission electron microscope; RSD, relative standard

384

deviation; MDL, Method detection limit; LOQ, limit of quantitation; CCV, continuing 18

ACS Paragon Plus Environment

Page 18 of 35

Page 19 of 35

Journal of Agricultural and Food Chemistry

385

calibration verification; ICV, initial calibration verification; RV, recovery value; DV, difference

386

value.

387

Acknowledgement

388

The views expressed in this manuscript are those of the authors and should not be interpreted as

389

the official opinion or policy of the U.S. Food and Drug Administration, Department of Health

390

and Human Services or any other agency or component of the U.S. government. The mention of

391

trade names, commercial products, or organizations is for clarification of the methods used and

392

should not be interpreted as an endorsement of a product or manufacturer. This research was

393

supported in part by an appointment to the Research Participation Program at the Office of

394

Regulatory Affairs/Arkansas Laboratory, U.S. FDA, administered by the Oak Ridge Institute for

395

Science and Education through an interagency agreement between the U.S. Department of

396

Energy and FDA.

397

Disclosure statement

398

No competing financial interests exist.

399

Conflict of interest

400

The authors declare that they have no conflict of interest.

401

Supporting Information

402

This material is available free of charge via the Internet at http://pubs.acs.org.

403

Particle extraction efficiency test and XRD characterization-FESEM images of before and after

404

extraction of TiO2 particles, and XRD peaks of anatase TiO2 before and after extraction; XRD 19

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

405

patterns of TiO2 particles with various ratio of anatase and rutile; Determination of ICP-MS

406

MDL and LOQ; ICP-MS calibration curve verification; CCV, ICV and spiked sample recovery

407

tests for ICP-MS; Raman calibration curve verification; Determination of Raman MDL and LOQ;

408

Raman spectra measured multiple times (n=10) at the same location of RS07 sample and the

409

corresponding peak height (h) of each scan at 143 cm-1; Raman spectra of anatase/rutile TiO2 and

410

anatase only TiO2 in Al2O3 matrix

20

ACS Paragon Plus Environment

Page 20 of 35

Page 21 of 35

Journal of Agricultural and Food Chemistry

References 1.

Jacobs, J. F.; van de Poel, I.; Osseweijer, P., Sunscreens with titanium dioxide (TiO2)

nano-particles: A societal experiment. Nanoethics 2010, 4, 103-113. 2.

Hong, F.; Yu, X.; Wu, N.; Zhang, Y.-Q., Progress of in vivo studies on the systemic

toxicities induced by titanium dioxide nanoparticles. Toxicol. Res. 2017, 6, 115-133. 3.

Ammendolia, M. G.; Iosi, F.; Maranghi, F.; Tassinari, R.; Cubadda, F.; Aureli, F.; Raggi,

A.; Superti, F.; Mantovani, A.; De Berardis, B., Short-term oral exposure to low doses of nanosized TiO2 and potential modulatory effects on intestinal cells. Food Chem. Toxicol. 2017, 102, 63-75. 4.

Skocaj, M.; Filipic, M.; Petkovic, J.; Novak, S., Titanium dioxide in our everyday life; is

it safe? Radiol. Oncol. 2011, 45, 227-247. 5.

Golja, V.; Dražić, G.; Lorenzetti, M.; Vidmar, J.; Ščančar, J.; Zalaznik, M.; Kalin, M.;

Novak, S., Characterisation of food contact non-stick coatings containing TiO2 nanoparticles and study of their possible release into food. Food Addit. Contam., Part A 2017, 34, 421-433. 6.

Corredor, C.; Borysiak, M. D.; Wolfer, J.; Westerhoff, P.; Posner, J. D., Colorimetric

detection of catalytic reactivity of nanoparticles in complex matrices. Environ. Sci. Technol. 2015, 49, 3611-3618. 7.

Goenaga-Infante, H.; Larsen, E. H., Characterisation of nanomaterials in biological

samples. Anal. Bioanal. Chem. 2014, 406, 3831-3833. 8.

Krug, H. F., Nanosafety research—Are we on the right track? Angew. Chem. Int. Ed.

Engl. 2014, 53, 12304-12319. 9.

Rauscher, H.; Rasmussen, K.; Sokull‐Klüttgen, B., Regulatory aspects of nanomaterials

in the EU. Chem. Ing. Tech. 2017, 89, 224-231. 21

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

10.

Dutschke, F.; Irrgeher, J.; Profrock, D., Optimisation of an extraction/leaching procedure

for the characterisation and quantification of titanium dioxide (TiO2) nanoparticles in aquatic environments using SdFFF-ICP-MS and SEM-EDX analyses. Anal. Methods 2017, 9, 3626-3635. 11.

Hsiao, I. L.; Bierkandt, F. S.; Reichardt, P.; Luch, A.; Huang, Y.-J.; Jakubowski, N.;

Tentschert, J.; Haase, A., Quantification and visualization of cellular uptake of TiO2 and Ag nanoparticles: comparison of different ICP-MS techniques. J. Nanobiotechnol. 2016, 14, 50. 12.

López-Heras, I.; Madrid, Y.; Cámara, C., Prospects and difficulties in TiO2 nanoparticles

analysis in cosmetic and food products using asymmetrical flow field-flow fractionation hyphenated to inductively coupled plasma mass spectrometry. Talanta 2014, 124, 71-78. 13.

Peters, R. J. B.; van Bemmel, G.; Herrera-Rivera, Z.; Helsper, H. P. F. G.; Marvin, H. J.

P.; Weigel, S.; Tromp, P. C.; Oomen, A. G.; Rietveld, A. G.; Bouwmeester, H., Characterization of titanium dioxide nanoparticles in food products: analytical methods to define nanoparticles. J. Agric. Food Chem. 2014, 62, 6285-6293. 14.

Pico, Y., Challenges in the determination of engineered nanomaterials in foods. Trends

Anal. Chem. 2016, 84, 149-159. 15.

Athinarayanan, J.; Alshatwi, A. A.; Periasamy, V. S.; Al-Warthan, A. A., Identification

of nanoscale ingredients in commercial food products and their induction of mitochondrially mediated cytotoxic effects on human mesenchymal stem cells. J. Food Sci. 2015, 80, N459N464. 16.

Faust, J. J.; Doudrick, K.; Yang, Y.; Westerhoff, P.; Capco, D. G., Food grade titanium

dioxide disrupts intestinal brush border microvilli in vitro independent of sedimentation. Cell Biol. Toxicol. 2014, 30, 169-188.

22

ACS Paragon Plus Environment

Page 22 of 35

Page 23 of 35

Journal of Agricultural and Food Chemistry

17.

Liu, M.; Piao, L.; Zhao, L.; Ju, S.; Yan, Z.; He, T.; Zhou, C.; Wang, W., Anatase TiO2

single crystals with exposed {001} and {110} facets: facile synthesis and enhanced photocatalysis. Chem. Commun. 2010, 46, 1664-1666. 18.

Bonnet, M.; Massard, C.; Veisseire, P.; Camares, O.; Awitor, K. O., Environmental

toxicity and antimicrobial efficiency of titanium dioxide nanoparticles in suspension. J. Biomater. Nanobiotechnol. 2015, 6, 213-224. 19.

Mudunkotuwa, I. A.; Anthony, T. R.; Grassian, V. H.; Peters, T. M., Accurate

quantification of tio(2) nanoparticles collected on air filters using a microwave-assisted acid digestion method. J. Occup. Environ. Hyg. 2016, 13, 30-39. 20.

Krystek, P.; Tentschert, J.; Nia, Y.; Trouiller, B.; Noël, L.; Goetz, M. E.; Papin, A.; Luch,

A.; Guérin, T.; de Jong, W. H., Method development and inter-laboratory comparison about the determination of titanium from titanium dioxide nanoparticles in tissues by inductively coupled plasma mass spectrometry. Anal. Bioanal. Chem. 2014, 406, 3853-3861. 21.

Faucher, S.; Lespes, G., Quantification of titanium from TiO2 particles in biological

tissue. J. Trace Elem. Med. Biol. 2015, 32, 40-44. 22.

Lim, J.-H.; Sisco, P.; Mudalige, T. K.; Sánchez-Pomales, G.; Howard, P. C.; Linder, S.

W., Detection and characterization of SiO2 and TiO2 nanostructures in dietary supplements. J. Agric. Food Chem. 2015, 63, 3144-3152. 23.

Bairi, V. G.; Lim, J.-H.; Quevedo, I. R.; Mudalige, T. K.; Linder, S. W., Portable X-ray

fluorescence spectroscopy as a rapid screening technique for analysis of TiO2 and ZnO in sunscreens. Spectrochim. Acta, part B 2016, 116, 21-27.

23

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

24.

Zhao, B.; Cao, X.; De La Torre-Roche, R.; Tan, C.; Yang, T.; White, J. C.; Xiao, H.;

Xing, B.; He, L., A green, facile, and rapid method for microextraction and Raman detection of titanium dioxide nanoparticles from milk powder. RSC Adv. 2017, 7, 21380-21388. 25.

Tan, C.; Zhao, B.; Zhang, Z.; He, L., Rapid detection of TiO2 (E171) in table sugar using

Raman spectroscopy. Food Addit. Contam., part A 2017, 34, 183-191. 26.

Lee, K.-M.; Herrman, T. J.; Yun, U., Application of Raman spectroscopy for qualitative

and quantitative analysis of aflatoxins in ground maize samples. J. Cereal. Sci. 2014, 59, 70-78. 27.

Ilie, A. G.; Scarisoareanu, M.; Morjan, I.; Dutu, E.; Badiceanu, M.; Mihailescu, I.,

Principal component analysis of Raman spectra for TiO2 nanoparticle characterization. Appl. Surf. Sci. 2017, 417, 93-103. 28.

Numata, Y.; Tanaka, H., Quantitative analysis of quercetin using Raman spectroscopy.

Food. Chem. 2011, 126, 751-755. 29.

Li, Y.-S.; Church, J. S., Raman spectroscopy in the analysis of food and pharmaceutical

nanomaterials. J. Food Drug Anal. 2014, 22, 29-48. 30.

Killeen, D. P.; Sansom, C. E.; Lill, R. E.; Eason, J. R.; Gordon, K. C.; Perry, N. B.,

Quantitative Raman spectroscopy for the analysis of carrot bioactives. J. Agric. Food. Chem. 2013, 61, 2701-2708. 31.

Weng, S.; Wang, F.; Dong, R.; Qiu, M.; Zhao, J.; Huang, L.; Zhang, D., Fast and

Quantitative analysis of ediphenphos residue in rice using surface-enhanced Raman spectroscopy. J. Food Sci. 2018, 83, 1179-1185. 32.

Tan, Z.; Lou, T.-t.; Huang, Z.-x.; Zong, J.; Xu, K.-x.; Li, Q.-f.; Chen, D., Single-drop

Raman imaging exposes the trace contaminants in milk. J. Agric. Food Chem. 2017, 65, 62746281. 24

ACS Paragon Plus Environment

Page 24 of 35

Page 25 of 35

Journal of Agricultural and Food Chemistry

33.

Zhao, B.; Yang, T.; Zhang, Z.; Hickey, M. E.; He, L., A triple functional approach to

simultaneously determine the type, concentration, and size of titanium dioxide particles. Environ. Sci. Technol. 2018, 52, 2863-2869. 34.

Dudefoi, W.; Moniz, K.; Allen-Vercoe, E.; Ropers, M.-H.; Walker, V. K., Impact of food

grade and nano-TiO2 particles on a human intestinal community. Food Chem. Toxicol. 2017, 106, 242-249. 35.

Re‐evaluation of titanium dioxide (E 171) as a food additive. EFSA J. 2016, 14, e04545.

36.

Lim, J.-H.; Bairi, V. G.; Fong, A., Quantification of impurities in carbon nanotubes:

Development of ICP-MS sample preparation methods. Mater. Chem. Phys. 2017, 198, 324-330. 37.

Summary of color additives for use in the United States in foods, drugs, cosmetics, and

medical devices, https://www.fda.gov/ForIndustry/ColorAdditives/ColorAdditiveInventories/ucm115641.htm#ftn ote1 (accessed July 12, 2018). 38.

Rompelberg, C.; Heringa, M. B.; van Donkersgoed, G.; Drijvers, J.; Roos, A.;

Westenbrink, S.; Peters, R.; van Bemmel, G.; Brand, W.; Oomen, A. G., Oral intake of added titanium dioxide and its nanofraction from food products, food supplements and toothpaste by the Dutch population. Nanotoxicology 2016, 10, 1404-1414. 39.

Liu, X.; Smith, M. E.; Tse, S. D., In situ Raman characterization of nanoparticle aerosols

during flame synthesis. Appl. Phys. B 2010, 100, 643-653. 40.

Liu, F. L.; Yan, X. D.; Chen, X. J.; Tian, L. H.; Xia, Q. H.; Chen, X. B., Mesoporous

TiO2 nanoparticles terminated with carbonate-like groups: Amorphous/crystalline structure and visible-light photocatalytic activity. Catal. Today 2016, 264, 243-249.

25

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

41.

Carlucci, C.; Xu, H.; Scremin, B. F.; Giannini, C.; Altamura, D.; Carlino, E.; Videtta, V.;

Conciauro, F.; Gigli, G.; Ciccarella, G., Selective synthesis of TiO2 nanocrystals with morphology control with the microwave-solvothermal method. CrystEngComm 2014, 16, 18171824. 42.

Zięba-Palus, J.; Michalska, A., Photobleaching as a useful technique in reducing of

fluorescence in Raman spectra of blue automobile paint samples. Vib Spectrosc 2014, 74, 6-12. 43.

Food additives permitted for direct addition to food for human consumption, U. S. FDA

21CFR172.480 silicon dioxide https://www.accessdata.fda.gov/scripts/cdrh/cfdocs/cfCFR/CFRSearch.cfm?fr=172.480 (accessed July 12, 2018). 44.

Bairi, V. G.; Lim, J.-H.; Fong, A.; Linder, S. W., Size characterization of metal oxide

nanoparticles in commercial sunscreen products. J. Nanopart. Res. 2017, 19, 256.

26

ACS Paragon Plus Environment

Page 26 of 35

Page 27 of 35

Journal of Agricultural and Food Chemistry

Table 1. List of Food Products Investigated in this Study, Summarizing the Particle Size, Size Distribution, and Concentrations (%) of TiO2 Food ID Category

Labela

Particle size (nm) (mean±SD)

Particles with less than 100 nm (%)b

Particle size distribution (nm)c

% TiO2 concentration (mean±SD) ICP-MS Raman

%RV2

%DV

RS01

Coffee Cream

Titanium dioxide (color)

141.7±54.3

24.2

40.3-391.3

0.111±0.005

0.126±0.010

113.5

12.7

RS02

Coffee Cream

Titanium dioxide (artificial color)

131.0±51.0

29.4

33.5-318.4

0.140±0.001

0.152±0.043

108.6

8.2

RS03

Cookie

Color added

107.8±39.9

49.8

31.1-286.1

0.185±0.003

0.195±0.110

102.0

2.0

RS04

Yogurt snack

Titanium dioxide

104.8±42.1

53.7

30.7-328.0

0.300±0.002

0.271±0.028

90.3

-10.2

RS05

Yogurt snack

Titanium dioxide

131.5±49.8

28.3

26.9-348.4

0.192±0.005

0.209±0.026

108.9

8.5

Yogurt beverage Hard candy Hard candy

Titanium dioxide (E171)

117.0±55.3

41.0

32.2-463.2

0.015±0.001

0.013±0.002

86.7

-14.3

Titanium dioxide

125.3±47.9

34.0

36.8-310.4

0.051±0.009

0.057±0.003

111.8

11.1

Titanium dioxide (for color)

123.1±47.2

34.8

30.1-307.3

0.275±0.003

0.314±0.013

114.2

13.2

RS09 Chocolate

Titanium dioxide

103.5±34.3

50.4

29.8-244.0

0.462±0.025

0.403±0.081

87.2

-13.6

RS06 RS07 RS08

RS010

Chewy candy

Titanium dioxide

147.8±57.9

21.3

37.2-439.2

0.028±0.004

0.032±0.001

114.3

13.3

RS011

Chewy candy

Titanium dioxide

120.4±48.9

40.3

29.9-326.1

0.025±0.001

0.029±0.001

116.0

14.8

aLabeling

of TiO2 found on products. bTiO nanoparticles with at least one dimension less than 100 nm. The values 2 cSize ranges of the smallest and largest TiO particles found on TEM images. 2

correspond to TEM results in Figure 2.

27

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 28 of 35

Table 2. Comparison of ICP-MS and Raman Values of TiO2 Working Standards Standard

standard known value (% TiO2)

ICP-MS (mean±SD)

Raman

%RV1

%RV2

%DV

1

1.159

1.130±0.001

1.066

91.9

94.3

-5.55591

2

1.067

1.030±0.003

1.095

102.6

106.3

6.137609

3

1.242

1.260±0.003

1.249

100.5

99.1

-0.51759

28

ACS Paragon Plus Environment

Page 29 of 35

Journal of Agricultural and Food Chemistry

Table 3. Spiked Sample Recovery Test for Raman Analysis Sample

Spiked sample known value (% TiO2)

Raman results (% TiO2)

%RV1

1

0.932

1.065

114.3

2

1.161

1.275

109.8

3

1.462

1.711

117.0

4

1.063

1.237

116.3

5

1.120

1.201

107.2

Average

112.9

29

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Figure Captions Figure 1. XRD patterns of TiO2 isolated from RS01-RS11. Figure 2. TEM images and size distribution histograms of TiO2. The number of TiO2 particles measured for the size distribution analysis was more than 350 for each sample (scale bar=200 nm). Figure 3. (A) Raman spectra and (B) calibration curve with six independent TiO2 working standards (anatase phase). Figure 4. Comparison of Raman spectra: (A) Al2O3 matrix, (B) mixture of anatase TiO2 and SiO2 in Al2O3 (the percent concentration of TiO2 and SiO2 is 1.5% and 1.98%, respectively), (C) anatase TiO2 in Al2O3 (1.8% of TiO2), (D) anatase, (E) rutile and (F) SiO2.

30

ACS Paragon Plus Environment

Page 30 of 35

Page 31 of 35

Journal of Agricultural and Food Chemistry

Figure 1

31

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Figure 2

32

ACS Paragon Plus Environment

Page 32 of 35

Page 33 of 35

Journal of Agricultural and Food Chemistry

Figure 3

33

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Figure 4

34

ACS Paragon Plus Environment

Page 34 of 35

Page 35 of 35

Journal of Agricultural and Food Chemistry

Table of Contents (TOC)

35

ACS Paragon Plus Environment