Accepted Manuscript Title: Acrylamide in commercial potato crisps from spanish market. Trends from 2004-2014 and assessment of the dietary exposure Author: Marta Mesías, Francisco J. Morales PII: DOI: Reference:

S0278-6915(15)00124-6 http://dx.doi.org/doi:10.1016/j.fct.2015.03.031 FCT 8278

To appear in:

Food and Chemical Toxicology

Received date: Accepted date:

2-2-2015 30-3-2015

Please cite this article as: Marta Mesías, Francisco J. Morales, Acrylamide in commercial potato crisps from spanish market. Trends from 2004-2014 and assessment of the dietary exposure, Food and Chemical Toxicology (2015), http://dx.doi.org/doi:10.1016/j.fct.2015.03.031. This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.

1

ACRYLAMIDE

2

MARKET. TRENDS FROM 2004-2014 AND ASSESSMENT OF THE DIETARY

3

EXPOSURE

IN

COMMERCIAL

POTATO

CRISPS

FROM

SPANISH

4 5

Marta Mesías*, Francisco J. Morales

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Institute of Food Science, Technology and Nutrition, ICTAN-CSIC, 28040-Madrid, Spain

8 9 10 11

Keywords: potato crisps, acrylamide, dietary intake, exposure, trend

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* Corresponding author. Institute of Food Science, Technology and Nutrition, ICTAN-

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CSIC, José Antonio Novais 10, 28040 Madrid, Spain. Tel.: +34 91 549 2300; fax: +34 91

15

549 3627

16

E-mail address: [email protected] (M. Mesías)

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Abbreviations: AECOSAN, Spanish Agency of Consumption and Food Security and

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Nutrition; BMD, Benchmark dose; BMDL, benchmark dose lower confidence limit; BW,

20

body weight; EC, European Commission; EFSA, European Food Safety Authority;

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EUPPA, European Association for Potato Transformers; FAO, Food and Agriculture

22

Organization; FAPAS, Food Analysis Performance Assessment Scheme; IARC,

23

International Agency for Research on Cancer; JECFA, Joint FAO/WHO Expert Committee

24

on Food Additives; LOQ, limit of quantification; MAGRAMA, Ministry of Agriculture,

25

Food and Environment; MOE, margin of exposure; WHO, World Health Organization.

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Highlights

28

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Acrylamide content in potato crisps ranged from 108 to 2180 µg/kg (mean: 630 µg/kg)

29

-

High variations were observed between batches for certain brands

30

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Acrylamide content in potato crisps showed a decreased trend from 2004 to 2014

31

-

Exposure to acrylamide from potato crisps was estimated to be 0.035 µg/kg BW/day

32

Abstract

33

This research updates the acrylamide content of commercial potato crisps marketed in

34

Spain with the aim to evaluate its trend since 2004. Two different batches of 40 potato

35

crisps brands from 18 producers were analysed. Acrylamide content ranged from 108 to

36

2180 µg/kg, with an average value of 630 µg/kg and a median of 556 µg/kg. Data revealed

37

a continuous decreased trend from 2004 to 2014. In 2014, potato crisps showed an average

38

acrylamide content 14.6% lower than the previous report in 2009 and 57.6% lower than the

39

first report in 2004. These data confirm the overall effectiveness in the mitigation strategies

40

implemented by the Spanish industrial sector, although variations up to 80% were observed

41

between a number of brands. However, the 17.5% of the samples registered values higher

42

than the indicative value recommended by European Commission for potato crisps. The

43

dietary exposure to this contaminant by Spanish population through the potato crisps intake

44

was estimated to be 0.035 µg/kg body weight/day. Although exposure has decreased over

45

the last ten years, it is necessary to continue efforts to reduce acrylamide content in potato

46

crisps since there is still margin for it.

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1.

Introduction

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Acrylamide is a process contaminant generated in several foods during cooking as a

51

consequence of the Maillard reaction, derived from the reaction between the free amino

52

acid asparagine with reducing sugars or other carbonyl compounds (Mottram and

53

Wedzicha, 2002). This chemical reaction mainly occurs when foods are subjected to high

54

temperatures as during frying, roasting or baking (Tareke et al., 2002), and in low moisture

55

conditions (Stadler et al., 2004). According to the European Food Safety Agency (EFSA),

56

processed potatoes together with coffee and cereal based food (cookies, crackers, breakfast

57

cereals and toasted bread), are the main sources of exposure to acrylamide in the diet

58

(EFSA, 2014). Due to the natural presence of large concentration of acrylamide precursors

59

in the potato, when this product is subjected to high temperatures, as during frying,

60

acrylamide is generated (Williams et al., 2005). Levels of this contaminant by up to 3000 or

61

even more than 4000 µg/kg have been detected in potatoes chips and crisps (Friedman et

62

al., 2003; Hilbig et al., 2004; Shamla and Nisha, 2014; Becalski et al., 2010).

63

It is known that dietary habits have changed over the last few years, increasing the

64

consumption of processed foods and decreasing this of natural foods (Delgado-Andrade,

65

2014). Such dietary changes are particularly evident in younger generations whose habits

66

are associated with high levels of snacking and fast food consumption which contributes to

67

high levels of acrylamide intake (Gilbert and Khokhar, 2008; Delgado-Andrade et al.,

68

2012). Among snacks foods, potato chips are one of the most popular foodstuffs and large

69

quantities are consumed in worldwide, especially by young people (Ouhtit et al., 2014;

70

Wyka et al., 2015). According to Katz et al. (2012) French fries and potato chips may

71

contribute 56% of the total acrylamide intake in the Western diet of the adolescents. Due to

72

this fact, recent researches have been focused on different aspects affecting acrylamide 4

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formation in fried potato products and possible mitigation strategies, which could be

74

summarized in two approaches: 1) to control acrylamide precursors in the fresh product

75

and, 2) to control the thermal treatment conditions applied during processing (Medeiros

76

Vinci et al., 2012). Authorities and producers have invested great efforts in mitigating

77

acrylamide formation and reducing acrylamide concentration in processed potatoes

78

(Biedermann et al., 2010). In this respect, reductions in the acrylamide content in potato

79

chips/crisps as compared with previous results have been reported by several authors

80

(Arribas-Lorenzo et al., 2009; Biederman et al., 2010; Cressey et al., 2012).

81

The aim of the present investigation was to determine the acrylamide content of

82

commercial potato crisps marketed in Spain as a major source of acrylamide in the diet.

83

Results were compared with data previously reported by our research group since 2004, in

84

order to evaluate the trend in the acrylamide content in Spanish potato crisps over the last

85

years and the effectiveness of the mitigation strategies. Finally, it was conducted an

86

assessment of the dietary exposure to this contaminant by Spanish population through the

87

potato crisps intake.

88 89

2.

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2.1. Chemicals and materials

Materials and methods

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Acrylamide standard (99%), potassium ferrocianide (Carrez I), and zinc acetate

92

(Carrez-II) and methanol (HPLC grade) were purchased from Sigma-Aldrich (St. Louis,

93

MO, USA). [13C3]-acrylamide (isotopic purity 99%) was from Cambridge Isotope Labs

94

(Andover, MA, USA). Acetic acid was from Merck (Darmstads, Germany) and hexane

95

from Panreac (Madrid, Spain). Milli-Q water used was produced using an Elix3 Millipore 5

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water purification system coupled to a Milli-Q module (model Advantage10) (Millipore,

97

Molsheim, France). All other chemicals, solvents and reagents were of analytical grade.

98

Reversed-phase Oasis-HLB cartridges (30 mg, 1 mL) were from Waters (Milford, MA,

99

USA). Syringe filter units (0.45 µm, cellulose) were purchased from Análisis Vínicos

100

(Tomelloso, Ciudad Real, Spain).

101

2.2. Samples

102

Two different batches from 40 brands of commercial potato crisps from 18 producers

103

were purchased in different Spanish supermarkets in September 2014. Samples containing

104

different flavourings and/or added spices were excluded for the sampling. Initially, ten

105

slices of potato crisps samples were randomly selected from each container and weighed in

106

order to calculate the mean weight of one slice of potato crisp. After that, samples (200–

107

500 g, according to the size of the bag) were mixed and grounded to assure a homogeneous

108

distribution of potential hotspots. A portion (100-200 g) was distributed in two containers

109

and stored under vacuum and light protected at 4ºC until analysis. Eighty different samples

110

were therefore individually analysed by duplicate.

111

2.3. Colour determination

112

Colour parameters were expressed according to CIE L*a*b* scale (CIE Colorimetric

113

Committee, 1974; McLaren & Riggs, 1976). The measurements were made using a

114

HunterLab Spectrophotometer CM-3500D colorimeter (Hunter Associates laboratory,

115

Stamford, Connecticut, USA). Three independent measurements of a*(redness),

116

b*(yellowness) and L*(lightness) parameters were carried out on different areas of the

117

grounded potato crisps. E index, C index and Y index were calculated according to the 6

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following equations: E = (L2 + a2 + b2)1/2; C = (a2 + b2)1/2; Y = 142.86b/L, which allows

119

evaluating the colour changes in the potato samples (Giangiacomo and Messina, 1988).

120

2.4. LC-ESI-MS-MS determination of acrylamide

121

Sample extraction and clean up were based on the method described by Morales et al.

122

(2007) with some modifications. Grounded sample (0.500 g) was weighed and mixed with

123

9.4 mL of water in polypropylene centrifugal tubes. Two mL of hexane were added in the

124

tubes in order to remove the fat content of the potato crisps. Mixture was spiked with 100

125

µL of a 5 µg/mL [13C3]-acrylamide methanolic solution as internal standard and later

126

homogenized (Ultra Turrax, IKA, Mod-T10 basic, Germany) for 10 min. Afterwards,

127

sample was treated with 250 µL of each Carrez I (15 g potassium ferrocianide/100 mL

128

water) and Carrez II (30 g zinc acetate/100 mL water) solutions and centrifuged (9,000g for

129

10 min) at 4ºC. Hexane was removed and samples were cleaned up by using of Oasis-HLB

130

cartridges. Cartridges were preconditioned with 1 mL methanol and 1 mL water. An aliquot

131

of the clear supernatant (1 mL) was loaded onto the cartridge at a flow rate of 2 mL/min

132

and first drops were discharged and the rest collected. Solution was filtered through a 0.45

133

µm filter into an amberlite LC–MS vial.

134

Sample extracts and calibration standards were analysed on an Agilent 1200 liquid

135

chromatograph coupled to an Agilent Triple Quadrupole MS detector (Agilent

136

Technologies, Palo Alto, CA, USA). Analytical separation was achieved with an Inertsil

137

ODS-3 column (250 x 4.6 mm, 5 µm; GL Sciences Inc., Tokio, Japan) at 30ºC. Isocratic

138

elution was achieved with a mobile phase of formic acid in water (0.2 mL/100 mL) at a

139

flow rate of 0.4 mL/min. The injection volume was 10 μL. Electrospray ionization in the

140

positive ionization mode was used. Under these chromatographic conditions, acrylamide 7

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eluted at 6.1 min. The needle was set at 1.0 kV. Nitrogen was used as nebulizer gas (12.0

142

L/min) and the source temperature was set at 350ºC. Signals at m/z 72.1 - m/z 55.1 and m/z

143

75.1 - m/z 58.1 were isolated for acrylamide and [13C3]-acrylamide, respectively. For the

144

transitions m/z 72.1 > m/z 55.1 and m/z 75.1 > m/z 58.1 the fragmentation was set at 76 V

145

and the collision energy at 8 V. Masses were recorded using multiple reactions monitoring

146

(MRM). For quantitation the signals at m/z 75.1 and 78.1 were used, while signals at m/z

147

58.1 and 55.1 served for qualification.

148

Acrylamide was quantified with standard solutions (5-100 µg/L) spiked with 50 µg/L

149

[13C3]-acrylamide. The peak identity is confirmed by comparison of the peak area ratios for

150

the transitions m/z 72 > 55 and 75 > 58 from sample extracts and standard solutions,

151

respectively. The limit of the quantitation was set at 20 µg/kg. The accuracy of the results

152

was recently demonstrated for potato crisps in an interlaboratory comparison study

153

launched by the Food Analysis Performance Assessment Scheme (FAPAS) program

154

(2013), yielding a z-score of 0.3. Precision (reproducibility) was lower than 10% and

155

recovery between 84 and 109%. Analysis was performed in duplicate and results were

156

expressed as µg/kg of product.

157

2.5. Food consumption data

158

Dietary intake of acrylamide from potato crisps was estimated by using the national

159

consumption database produced by the Ministry of Agriculture, Food and Environment

160

(MAGRAMA, 2010). For this purpose, annual data are obtained from households, hotels

161

and restaurants, and also from institutions such as schools, hospitals and the armed forces.

162

These sources make it possible to classify significant changes in dietary patterns and

163

constitute the most reliable means available for estimating food consumption in Spain 8

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(Varela Moreiras et al., 2007). Data collection is carried out by questionnaires that include

165

daily notes on household food purchased, with monthly results for 12000 households. In

166

addition, monthly notes on food purchased in 1500 hotels and restaurants and in 300

167

institutions are carried out by specialist interviewers, with trimester results (MAGRAMA,

168

2010).

169

In the present study, information about processed potatoes consumption data reported

170

for the year 2010 (million kg per year) was used. Data expressed as kg per capita has been

171

calculated, taking into account the population in Spain for this year. An average body

172

weight (BW) of 70 kg was used to estimate the total daily intake of acrylamide from

173

processed potatoes for the total population and expressed as µg/kg BW/day.

174

2.6. Statistical analysis

175

Statistical analyses were performed using Statgraphics Centurion XV (Herndon, VA,

176

USA). Data were expressed as mean ± standard deviation (SD). Analysis of variance

177

(ANOVA) and Student’s t test were applied to determine significant differences between

178

means. Differences were considered to be significant at p < 0.05. Relationships between the

179

different parameters analysed were evaluated by computing Pearson linear correlation

180

coefficients at the p < 0.05 confidence level.

181 182

3.

183

3.1. Acrylamide content in potato crisps

Results and discussion

184

In the present study, two different batches from 40 classical potato crisps brands,

185

without flavour or species added, from 18 different Spanish producers were analysed for 9

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the determination of acrylamide content (n = 80). Acrylamide content ranged from 108 to

187

2180 µg/kg, with an average value of 630 µg/kg and a median of 556 µg/kg (Table 1).

188

These results are in concordance with those reported by other authors, who found data

189

ranging from 591 to 1999 µg/kg (Arisseto et al., 2009), 430-1100 µg/kg (Wong et al., 2014)

190

or 244-1688 µg/kg (Boroushaki et al., 2010), being lower than other values described in

191

potato chips from Indian (82.0-4245.5 µg/kg, Shamla and Nisha, 2014) or Canadian market

192

(106-4630 µg/kg, Becalski et al., 2010). Similarly, both mean and median are close to the

193

values published by EFSA in 2010 for the category of potato crisps from fresh potatoes

194

(mean: 758 µg/kg; median: 543 µg/kg), and the highest content observed in our dataset was

195

lower than that reported by EFSA (4533 µg/kg) (EFSA, 2011).

196

The acrylamide distribution in the forty brands from potato crisps marketed in Spain is

197

shown in Fig. 1, where each value represents the mean ± standard deviation from the two

198

different batches analysed for the same brand. All the crisps contained acrylamide levels

199

higher than the limit of quantification (LOQ = 20 µg/kg). It is noticeable the identification

200

of two outliers in the distribution. Data distribution shown the high variability in the

201

acrylamide content among samples, which is likely the result of the unsatisfactory raw

202

material used and/or processing conditions applied. It is not the aim of this investigation to

203

describe the mitigation strategies applied for potato products and exhaustively reviewed

204

somewhere (Medeiros Vinci et al., 2012)

205

The application of signal values (P90, percentile 90) is useful for companies to monitor

206

the success during application of the mitigation strategies, if any. This concept can be

207

applied to the whole dataset. Three levels can be defined: acceptable (samples below the

208

P50), under evaluation (samples between P50-P90) and unacceptable (samples above P90).

209

P90 is identified as the signal value of the dataset and points out the reference value from 10

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which actions might be taken to low the acrylamide levels in these products. In our

211

investigation, 10% of the samples overcome the signal value (1169 µg/kg), as depicted in

212

Fig. 1.

213

Another reference used for quality control is considering the indicative values

214

recommended by the European Commission (EC). EC has recently adopted new indicative

215

acrylamide values based on the EFSA monitoring data from 2007-2012 for the main

216

sources of acrylamide exposure. These recommendations involve reference values for

217

acrylamide content in the major contributors to the intake of this compound. In cases where

218

the level of acrylamide in a foodstuff exceeds the acrylamide indicative value set for the

219

respective food category according to the recommendation, investigations into the

220

production and processing methods used by food producers must be carried out. Thereby,

221

risk associated with the acrylamide intake can be regulated and, consequently, controlled.

222

Indicative acrylamide value for potato chips according to the latest EC Recommendation of

223

8 November 2013 (2013/647/EU) is reported to be 1000 µg/kg (EC, 2013). In the present

224

study seven of the brands analysed exceed this indicative value, which means that

225

additional efforts should be implemented by this companies in order to decrease acrylamide

226

levels in their samples.

227

Additional information about the samples was taken into account to establish the

228

possible relationship with the acrylamide content. In this respect, samples were classified

229

according to (1) the presence or not of oil drops on the container layer after visual

230

inspection (oily, medium oily, not oily), (2) type of frying oil based on the information

231

provided by the manufacturer (sunflower oil, olive oil and other or undefined oil), (3) light

232

protection of the container (light-, partly light- or not light-protected) and (4) packaging

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under protective atmosphere (with or without protective atmosphere), as described in Table

234

1. In addition, price (EUR/100 g) of the potato samples was also considered as variable.

235

Statistically significant differences (p < 0.05) were observed respect to the presence of

236

oil drops on the container, where higher oil drops observed by consumer, higher acrylamide

237

level. Type of frying oil used and protective packaging, however, were not directly related

238

with the acrylamide content in the potato crisps. The price of the container ranged from

239

0.33 to 1.40 EUR/100 g (mean: 0.75 ± 0.27 EUR/100 g). Only one of the batches from one

240

of the 40 brands analysed showed a discordant result if price and acrylamide are correlated.

241

Surprisingly, a significant negative correlation between both parameters was observed (p =

242

0.0198, r2 = -0.2617), which involves that more expensive samples were associated with

243

lower levels of the process contaminant. This observation probably could be associated

244

with the fact that the largest companies, whose products may be more expensive, applied

245

more effectively the mitigation strategies than the smaller companies. In that sense, the cost

246

for the implementation of the mitigation strategies is reflected in the price for consumers.

247

Regarding colour parameters, means of E index, C index and Y index were calculated

248

to be 68.14 ± 2.11, 26.72 ± 1.84 and 0.75 ± 0.27, respectively. Colour of the samples was

249

also related with the acrylamide content. Thereby, acrylamide concentrations were

250

positively correlated with Y index (p = 0.0036, r2 = 0.3260) and negatively correlated with

251

E index (p = 0.0016, r2 = -0.3468), which would be expected due to more severe frying

252

treatment and the formation of brown pigments in the advance of the Maillard reaction

253

would involve loss of lightness and progress of the colour in the red zone (Pedreschi et al.,

254

2006). However, it is important to highlight that colour parameters are not expressed as

255

increment since the original potato tuber was not available.

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A relevant aspect to be considered is the difference observed between the batches for a

257

same brand of potato crisps. Two different batches from each commercial brand were

258

analysed. In the case of the differences between batches were higher than 20%, analyses

259

were repeated to confirm the results. Fig. 2 shows the distribution in number of cases of

260

percentage of the variation found between acrylamide content of the two different batches

261

for a same commercial brand. The variability among batches, expressed as coefficient of

262

variation (CV), ranged from 1.5% to 83.8%. Most of the samples reported differences

263

among batches lower than 20%. However it must be emphasized that 40% of the samples

264

presented variations higher than 20%, highlighting eight samples displaying variations

265

among batches in the range of 50-80% and another one with batches presenting differences

266

even higher than 80%. Similar observations have been reported by Cressey et al. (2012) in

267

potato chips from New Zealand, where some brands were extremely consistent across

268

batches while concentrations for acrylamide detected in other brands varied considerably

269

(range 371-1460 μg/kg). The results indicate that the products vary considerably in the

270

amount of acrylamide due to differences in the potato tuber and processing/manufacturing

271

conditions during the industrial process.

272

Fig. 3 shows the mean and standard deviation of the acrylamide concentration for the

273

18 producers in the potato crisps analysed in the current study. Even though different

274

number of brands were analysed per producer, it is interesting to mark that the acrylamide

275

content of some potato crisp producers were notably more variable than others. Acrylamide

276

concentrations varied from brands to brands, but also within some producers. For instance,

277

producers 1 and 6, both providing 2 batches x 7 different brands, exhibited totally different

278

results; while results for acrylamide content in potato crisps from the producer 6 ranged

279

from 145 to 1332 µg/kg, values for samples from the producer 1 were very close (range: 13

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145-432 µg/kg), involving low variability in the levels of acrylamide among both batches

281

and brands. In agreement with Cressey et al. (2012), the small deviations observed for some

282

brands support the statement that it is possible for a crisp manufacturer to produce a

283

consistent product with respect to acrylamide content.

284

3.2. Trends in acrylamide levels

285

Successful mitigation achievements of acrylamide levels in potato crisps and chips

286

have been reported by several authors in some countries during the last few years.

287

Biederman et al. (2010) explored the acrylamide content in potato chips from Switzerland

288

and observed that levels of the contaminant, evaluated from April 2007 to December 2009,

289

were diminished from 6900 µg/kg to 420 µg/kg over the years. In studies carried out in

290

New Zealand the range of acrylamide concentration in potato crisps decreased from 370-

291

2320 µg/kg in 2006 (Love and Grounds, 2006) to 112-1460 µg/kg in 2012 (Cressey et al.,

292

2012), possibly due to the application of mitigation measures by potato chips industries. In

293

a similar way, average acrylamide levels in German potato crisps produced from stored

294

potatoes decreased from the range of 800–1000 μg/kg in 2002–2003 to 400–600 μg/kg in

295

2004–2009 (WHO, 2011). Recently Powers et al. (2013) evaluated the acrylamide

296

concentrations in potato crisps in Europe from 2002 to 2011, observing a decrease in the

297

levels of the contaminant from 763 µg/kg in 2002 to 358 µg/kg in 2011. Overall the study

298

demonstrated the effectiveness of the approaches taken by potato crisp manufactures to

299

reduce acrylamide levels in their products. On the contrary, this downward trend in

300

acrylamide levels in potato crisps was not shown in data compiled by the EFSA (EFSA,

301

2012). In this report, mean acrylamide level of 570 µg/kg in 2007 was slightly increased to

302

758 µg/kg in 2010, suggesting, therefore, the limited evidence of active mitigation efforts. 14

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In the present study levels of acrylamide in potato crisp marketed in Spain in 2014

304

were compared with data previously reported by our group research in 2004 (Rufián-

305

Henares et al., 2006) and 2009 (Arribas-Lorenzo and Morales, 2009). In the 2004 sampling,

306

potato crisps showed a mean and median of 1484 µg/kg and 1180 µg/kg, respectively

307

(range: 211-5492 µg/kg). Nearly a 50% reduction was reached in the 2009 study, reporting

308

a mean content of 740 µg/kg (range: 81-2622 µg/kg, median: 592 µg/kg). In the current

309

study, levels of acrylamide were reduced again as compared with the previous sampling

310

data. In 2014, mean acrylamide content was 14.6% lower than this from 2009 and 57.6%

311

lower than this from 2004. Values for the first and third quartiles were however very close

312

to those reported in 2009, all of them being diminished when compared with 2004 results.

313

Even though minimum vales detected were close in the three studies, maximum level was

314

substantially reduced over the years, which minimizes the heterogeneity of the distribution

315

(Fig. 4). Among the samples marketed in the present study, ten potato crisps brands were

316

also analysed in the previous 2009 sampling. Seven of these ten samples showed lower

317

acrylamide content in the current study compared with the previous results; the reduction

318

was between 22-66%. The remaining three samples showed practically the same results

319

than those reported in 2009. All these findings illustrate the effectiveness in the mitigation

320

strategies carried out to diminish acrylamide levels in potato products.

321

3.3. Acrylamide exposure from potato crisps

322

Exposure assessment was estimated from the latest national consumption database

323

available, containing data obtained from households, hotels, restaurants, and institutions

324

(MAGRAMA, 2010). During 2010, the total consumption of processed potatoes was 65.78

325

million kg/year, which represents an overall estimation of annual consumption of 1.43 kg 15

Page 15 of 29

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processed potato products per capita. Assuming an average body weight of 70 kg for adults,

327

the average contribution of potato crisps to dietary acrylamide exposure in Spain was

328

calculated to be 0.035 µg/kg BW/day. If minimum and maximum levels of acrylamide

329

quantified in the potato crisps of this experiment are considered, the range of acrylamide

330

exposure from these products would be 0.006-0.12 µg/kg BW/day. The mean value was

331

similar to those reported in other studies on adults from Latvia (Pugajeva et al., 2014) or the

332

UK (Mills et al., 2008), being higher than these from France (Sirot et al., 2012), Poland

333

(Mojska et al., 2010) or Hong Kong (Wong et al., 2014). With regard to the previous study

334

the annual consumption of processed potato products per capita in 2009 and 2014 are

335

similar but due to the mean of acrylamide levels in potato crisps have been found

336

decreased, the dietary acrylamide exposure of Spanish consumers has been reduced

337

(Arribas-Lorenzo et al., 2009). Table 2 describes the estimation of total dietary exposure to

338

acrylamide and the contribution calculated for potato chips and crisps as reported in

339

different studies. As can be observed the contribution of potato chips and crisps to the

340

dietary acrylamide exposure ranges from 1 to 46%.

341

For dietetics purposes, we consider useful to provide adequate information to

342

professionals in the nutrition area since these professionals use the concept of food

343

portions. Then, the mean weight of one slice of potato crisp was calculated by weighing ten

344

slices of potato crisps samples randomly selected from each container. This mean weight

345

was estimated to be 1.5 g/slice, which would involve an average of acrylamide intake of

346

0.94 µg/slice (range: 0.16-3.27 µg/slice).

347

The risk assessment for acrylamide in potato crisp was conducted according to the

348

harmonized approach of the EFSA (EFSA, 2005), which recommends the use of the margin

349

of exposure (MOE) based on the benchmark dose (BMD) as standardised reference point of 16

Page 16 of 29

350

departures (Benford et al., 2010). Likewise MOE is calculated for the most sensitive

351

carcinogenic effect of acrylamide by using the ratio of the reference point (BMDL10 when

352

using data from experimental animals) and a conservative estimate of human exposure

353

(JECFA, 2010). EFSA Scientific Committee on Contaminants in the Food Chain

354

(CONTAM Panel) adopted that an MOE above 10000 for a compound that is both

355

genotoxic and carcinogenic is considered of low health concern (EFSA, 2005) and would

356

not be a priority for risk management action (Barlow et al., 2006). The MOE calculated for

357

acrylamide in food is low and this may indicate a human health concern (EFSA, 2005).

358

In this respect, an MOE value of 8857 was obtained when comparing mean acrylamide

359

exposure with the established BMDL10 (310 µg/kg BW/day) for mammary tumours in

360

female rats. Similarly, an MOE value of 5143 was obtained when comparing with the

361

established BMDL10 (180 µg/kg BW/day) for Harderian gland tumours in male mice.

362

Former MOE values are just restricted to the contribution of the consumption of potato

363

crisp and are lower than the value of 10000 categorized by EFSA as low concern from a

364

public health point of view. It is worth commenting that it should be always considered the

365

uncertainty before any risk extrapolation since the confidence of the MOE estimation is

366

very much dependent on the quality of the dose–response and exposure information. The

367

dose–response data is derived from rodent bioassays where differences in species

368

toxicokinetics may have an impact on extrapolation to human exposure (Bolger et al.,

369

2010). These results are in line with data recently revised by EFSA (EFSA, 2014).

370

Therefore it is necessary to continue efforts to reduce acrylamide content in potato crisps

371

and, consequently, the dietary exposure to acrylamide.

372

17

Page 17 of 29

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4.

Conclusions

374

The present research reports acrylamide content in commercial potato crisps marketed

375

in Spain. Results were compared with data previously reported by our research group, in

376

order to evaluate the trend in the acrylamide content in Spanish potato crisps over the last

377

ten years and, subsequently to assess the effectiveness of the mitigation strategies over the

378

time. Results revealed a decreased trend in acrylamide content from 2004 to 2014, which

379

illustrates the effectiveness in the mitigation strategies carried out to diminish acrylamide

380

levels in potato products. However, it is noticeable the high variability among batches for

381

several brands. The dietary exposure to this contaminant by Spanish population through the

382

potato crisps intake was also estimated, concluding that, although exposure has decreased

383

over the last few years, it is therefore necessary to continue efforts to reduce acrylamide

384

content in potato crisps since it is technically realistic. These data are useful for risk

385

assessment purposes in the Spanish population.

386

Conflict of interest

387 388

The authors declare that there are no conflicts of interest. Acknowledgements

389

This research was partly funded by projects S1013/ABI-3028-AVANSECAL

390

(Comunidad Autónoma of Madrid and FEDER program) and CSIC-201370E027. Authors

391

wish to thank to Ms. H. Moreno for the technical assistance and to Ms. I. Alvarez and Mr.

392

MA. Martinez for their technical assistance with acrylamide analyses.

393

References

18

Page 18 of 29

394

Arisseto, A.P., de Figueiredo Toledo, M.C., Govaert, Y., van Loco, J., Fraselle, S.,

395

Degroodt, J.M., Rosseto Caroba, D.C., 2009. Contribution of selected foods to

396

acrylamide intake by a population of Brazilian adolescents. LWT - Food Sci. Technol.

397

42, 207–211.

398 399

Arribas-Lorenzo, G., Morales, F.J., 2009. Dietary exposure to acrylamide from potato crisps to the Spanish population. Food Addit. Contam. 26, 289–297.

400

Barlow, S., Renwick, A.G., Kleiner, J., Bridges, J.W., Busk, L., Dybing, E., et al., 2006.

401

Risk assessment of substances that are both genotoxic and carcinogenic report of an

402

international conference organized by EFSA and WHO with support of ILSI Europe.

403

Food Chem. Toxicol. 44, 1636–1650.

404

Becalski, A., Stadler, R., Hayward, S., Kotello, S., Krakalovich, T., Lau, B.P.Y., et al.,

405

2010. Antioxidant capacity of potato chips and snapshot trends in acrylamide content

406

in potato chips and cereals on the Canadian market. Food Addit. Contam. 27, 1193–

407

1198.

408

Benford, D., Bolger, P.M., Carthew, P., Coulet, M., DiNovi, M., Leblanc, J.C., et al., 2010.

409

Application of the Margin of Exposure (MOE) approach to substances in food that are

410

genotoxic and carcinogenic. Food Chem. Toxicol. 48, S2–S24.

411

Biedermann, M., Grundböck, F., Fiselier, K., Biedermann, S., Bürgi, C., Grob, K., 2010.

412

Acrylamide monitoring in Switzerland, 2007–2009: results and conclusions. Food

413

Addit. Contam. 27, 1352–1362.

414

Bolger , P.M., Leblanc, J.C., Setzer, R.W., 2010. Application of the Margin of Exposure

415

(MoE) approach to substances in food that are genotoxic and carcinogenic EXAMPLE:

416

Acrylamide (CAS No. 79-06-1). Food Chem. Toxicol. 48, S25-S33. 19

Page 19 of 29

417

Boroushaki, M.T., Nikkhah, E., Kazemi, A., Oskooei, M., Raters, M., 2010. Determination

418

of acrylamide level in popular Iranian brands of potato and corn products. Food Chem.

419

Toxicol. 48, 2581–2584.

420 421

CIE Colorimetry Committee, 1974. Technical notes: working program on colour differences. J. Opt. Soc. Am., 64, 896–897.

422

Claeys, W., Baert, K., Mestdagh, F., Vercammen, J., Daenens, P., De Meulenaer, B., et al.,

423

2010. Assessment of the acrylamide intake of the Belgian population and the effect of

424

mitigation strategies. Food Addit. Contam. 27, 1199–1207.

425

Cressey, P., Thomson, B., Ashworth, M., Grounds, P., McGill, E., 2012. Acrylamide in

426

New Zealand food and updated exposure assessment. MAF Technical Paper No:

427

2011/19.

428

.

430 431

Risk

Assessment

Studies.

Report

No.

43.

Delgado-Andrade, C., 2014. Maillard reaction products: some considerations on their health effects. Clin. Chem. Lab. Med. 52, 53–60.

432

Delgado-Andrade, C., Mesías, M., Morales, F.J., Seiquer, I., Navarro, M.P., 2012.

433

Assessment of acrylamide intake of Spanish boys aged 11e14 years consuming a

434

traditional and balanced diet. LWT - Food Sci. Technol. 46, 16–22.

435

EC, 2013. European Commission. Commission Recommendation of 8 November 2013 on

436

investigations into the levels of acrylamide in food. Official Journal of the European

437

Union 315-317. 12-11-13. L 301:15-17. .

439

EFSA, 2005. Statement on summary report on Acrylamide in food of the 64th meeting of

440

the joint FAO/WHO expert committee on food additives by the Scientific Panel on 20

Page 20 of 29

441

contaminants

442



443

EFSA, 2011. European Food Safety Authority. Results on acrylamide levels in food from

444 445

in

the

food

447

.

450 451 452 453 454 455

Parma.

EFSA, 2012. European Food Safety Authority. Update on acrylamide levels in food from monitoring

449

(CONTAM),

monitoring years 2007-2009. EFSA J. 4, 2133. .

446

448

chain

years

2007

to

2010.

EFSA

J.,

10:

2938.

EFSA, 2014. European Food Safety Authority. Draft Scientific Opinion on Acrylamide in Food. < http://www.efsa.europa.eu/en/consultations/call/140701.pdf> Friedman, M., 2003. Chemistry, biochemistry, and safety of acrylamide. A review. J. Agric. Food Chem. 51, 4504–4526. Giangiacomo, R., Messina, G., 1988. Determinazione oggettiva del colore del latte alimentare mediante colorimetro tristimolo. Sci. Tecn. Latt. Cas. 39, 20–39. Gilbert, P.A., Khokhar, S., 2008. Changing dietary habits of ethnic groups in Europe and implications for health. Nutr. Rev. 66, 203–215.

456

Hilbig, A., Freidank, N., Kersting, M., Wilhelm, M., Wittsiepe, J., 2004. Estimation of the

457

dietary intake of acrylamide in German infants, children and adolescents as calculated

458

from dietary records and available data on acrylamide levels in food groups. Int. J.

459

Hyg. Environ. Health 207, 463–471.

460

IARC, 1994. International Agency for Research on Cancer. Monographs on the evaluation

461

of carcinogenic risks to humans: Some industrial chemicals 60, 389–433. International

462

Agency for Research on Cancer, Lyon, France.

463

JECFA, 2005. Joint FAO/WHO Expert Committee on Food Additives. Summary and

464

conclusions of the Sixty-fourth Meeting of the Joint FAO/WHO Expert Committee on 21

Page 21 of 29

465

Food

466



Additives,

Rome,

Italy,

8–17

February

2005.

467

JECFA, 2010. Joint FAO/WHO Expert Committee on Food Additives. Summary report of

468

the Seventy-second Meeting of the JECFA. Rome, 16–25 February 2010.

469



470

Katz, J.M., Winter, C.K., Buttrey, S.E., Fadel, J.G., 2012. Comparison of acrylamide intake

471

from Western and guideline based diets using probabilistic techniques and linear

472

programming. Food Chem Toxicol 50, 877–883.

473 474 475

Love, J., Grounds, P., 2006. Chemical food safety. Acrylamide in New Zealand food. ESR Client Report FW0545. Christchurch: ESR. MAGRAMA, 2010. Ministry of Agriculture, Food and Environment. Datos de consumo

476

alimentario.

477

comercializacion-y-distribucion-alimentaria/panel-de-consumo-alimentario/ultimos-

478

datos/>.

479 480

Acrylamide in commercial potato crisps from Spanish market: Trends from 2004 to 2014 and assessment of the dietary exposure.

This research updates the acrylamide content of commercial potato crisps marketed in Spain with the aim to evaluate its trend since 2004. Two differen...
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