Absorption, Distribution, Metabolism and Excretion ... - ACS Publications

Mar 9, 2017 - Beijing Advanced Innovation Center for Food Nutrition and Human Health, Beijing Technology & Business University (BTBU),. Beijing 100048...
2 downloads 7 Views 693KB Size
Subscriber access provided by UB + Fachbibliothek Chemie | (FU-Bibliothekssystem)

Article

Absorption, distribution, metabolism and excretion of 3MCPD 1-monopalmitate after oral administration in rats Boyan Gao, Man Liu, Guoren Huang, Zhongfei Zhang, Yue Zhao, Thomas T. Y. Wang, Yaqiong Zhang, Jie Liu, and Liangli (Lucy) Yu J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.7b00639 • Publication Date (Web): 09 Mar 2017 Downloaded from http://pubs.acs.org on March 12, 2017

Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.

Journal of Agricultural and Food Chemistry is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.

Page 1 of 28

Journal of Agricultural and Food Chemistry

Absorption, distribution, metabolism and excretion of 3-MCPD 1-monopalmitate after oral administration in rats Boyan Gao1,2, Man Liu3, Guoren Huang3, Zhongfei Zhang3, Yue Zhao3, Thomas T.Y. Wang4, Yaqiong Zhang3, Jie Liu1*, Liangli (Lucy) Yu2*

1

Beijing Advanced Innovation Center for Food Nutrition and Human Health, Beijing

Technology & Business University (BTBU), Beijing 100048, China; 2Department of Nutrition and Food Science, University of Maryland, College Park, MD 20742; 3Institute of Food and Nutraceutical Science, School of Agriculture and Biology, Shanghai Jiao Tong University; 4Diet, Genomics, and Immunology Laboratory, Agricultural Research Service (ARS), USDA, Beltsville, MD 20705

*Corresponding author: Jie Liu and Liangli (Lucy) Yu Contact information of the corresponding author: Liangli (Lucy) Yu, Tel: (01) 301-314-3313, Email: [email protected]; Jie Liu, Tel: (086) 010-6898-4547, E-mail: [email protected]

1

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

1

Abstract

2

Fatty acid esters of monochloropropane 1,2-diol (3-MCPD) are processing-induced

3

toxicants and have been detected in several food categories. This study investigated

4

the absorption, distribution, metabolism and excretion of 3-MCPD esters in Sprague

5

Dawley (SD) rats using 3-MCPD 1-monopalmitate as the probe compound. The

6

kinetics of 3-MCPD 1-monopalmitate in plasma was investigated using (SD) rats, and

7

the results indicated that 3-MCPD 1-monopalmitate was absorbed directly in vivo and

8

metabolized. Its primary metabolites in the liver, kidney, testis, brain, plasma and

9

urine were tentatively identified and measured at 6, 12, 24 and 48 hours after oral

10

administration. Structures were proposed for 8 metabolites. 3-MCPD

11

1-monopalmitate was converted to free 3-MCPD, which formed the phase II

12

metabolites. All the metabolites were chlorine-related chemical components; most of

13

them existed in urine, reflecting the excretion pattern of 3-MCPD esters.

14

Understanding the metabolism of 3-MCPD esters in vivo is critical for assessing their

15

toxicities.

16 17

Key words: 3-MCPD ester; toxic kinetics; UPLC-MS; absorption, distribution,

18

metabolism and excretion (ADME)

2

ACS Paragon Plus Environment

Page 2 of 28

Page 3 of 28

Journal of Agricultural and Food Chemistry

19

Introduction

20

Fatty acid esters of 3-monochloropropane 1,2-diol (3-MCPD esters), a group of

21

chemical toxicants for kidney and testis, could be formed during oil refining process

22

and have been detected in many food categories including infant and baby foods.1-7 In

23

2004, 3-MCPD ester was first reported together with free 3-MCPD in the processed

24

foods, with the esters form in a much higher concentration, especially in oils and fats

25

as well as the fried foods.8 In 2013, the European Food Safety Authority estimated a

26

tolerable daily value (TDI) of 2 µg/kg body weight for the total amount of free

27

3-MCPD.9

28

Recent research has investigated the detection methods, the possible formation

29

mechanisms, and the toxicology of 3-MCPD esters in vivo and in vitro.10-13 In 2015,

30

Sawada and colleagues reported an overview of proteomic changes caused by

31

3-MCPD di-esters and free 3-MCPD in rat testis in an early phase of organ

32

impairment.14 Onami and colleagues reported the potential subchronic toxicity of two

33

3-MCPD di-esters and one 3-MCPD mono-ester to the rat kidneys and epididymis

34

after a repeated dose study for 13 weeks.15 Our group also reported the acute toxicity

35

of several 3-MCPD mono- and di-esters in mice and their cytotoxicity in rat kidney

36

cells.10 The results indicated that 3-MCPD mono-ester might have stronger toxicity

37

compared with di-esters. To our best knowledge, there is little information about the

38

absorption, distribution, metabolism and excretion (ADME) of 3-MCPD esters,

39

although these data are important to access the risk of 3-MCPD esters intake.

40

Absorption, distribution, metabolism and excretion (ADME) may alter the

3

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 4 of 28

41

pharmacokinetics of food components, and consequently influence their beneficial or

42

toxicological activities at a selected organ or tissue. Only few studies reported the

43

metabolism and metabonomic of 3-MCPD and its fatty acid esters in vivo and their

44

metabonomic results in the rat urine and the cultured cells.16-19 In 2013, Li and

45

colleagues reported that indoxyl sulfate, xanthurenic acid, phenylacetylglycine,

46

nonanedioic acid and taurine can be used as biomarkers and represent the

47

consumption of 3-MCPD esters in a long-term toxicity study.16 In 2015, Andreoli and

48

colleagues reported that 2,3-dihydroxypropyl mercapturic acid (DHPMA) was

49

detected and identified as the metabolite of free 3-MCPD in human urine.18 In 2016,

50

the metabolomic study of free 3-MCPD in Wistar rats was evaluated, the results

51

indicated that the metabolism of glycine, serine and threonine, as well as the

52

metabolism of taurine and hypotaurine, were two key pathways related with the

53

3-MCPD.19 Till now, no systemic research about the ADME situation of 3-MCPD

54

esters in vivo was reported. Due to this fact, a systematic study about the absorption,

55

distribution, metabolism and excretion of 3-MCPD esters in vivo was performed.

56

In this study, the absorption of 3-MCPD 1-monopalmitate in rat plasma was

57

quantified at different time points after oral administration of 3-MCPD

58

1-monopalmitate to rats. The relative concentrations of 3-MCPD 1-monopalmitate in

59

different organs and tissues as well as plasma and urine samples were also determined.

60

In addition, major metabolites of 3-MCPD 1-monopalmitate in rat liver, kidney, testis,

61

brain, plasma and urine were tentatively identified and relatively quantified. The

4

ACS Paragon Plus Environment

Page 5 of 28

Journal of Agricultural and Food Chemistry

62

results of this study suggested how 3-MCPD 1-monopalmitate might be excreted from

63

rats for the first time. These results could significantly advance our understanding

64

about the physiological and toxicological properties of 3-MCPD esters.

65 66 67

Materials and Methods Chemicals and reagents. 3-MCPD 1-monopalmitate was synthesized according

68

to a previously reported protocol13 and its purity was above 98% tested by

69

UPLC-Q-TOF MS analysis. LC-MS grade isopropanol and methanol were purchased

70

from Sigma-Aldrich (St. Louis, MO, USA). LC-MS grade water was obtained from a

71

Milli-Q 10 ultra-pure water system (Billerica, MA, USA). All the other chemical

72

reagents were analytical grade and purchased from Sigma-Aldrich (St. Louis, MO,

73

USA). The chemical reagents and solvents were used without further purification.

74

Animals, treatment and sample collection. The animal study protocols were

75

approved by the Animal Ethics Committee of the Shanghai Jiao Tong University.

76

Male Sprague-Dawley rats, weighing 160-180 g, were bought from SLAC

77

experimental animal Co. Ltd (Shanghai, China). The rats were maintained in a

78

temperature controlled room with a 12 h light/dark cycle, and were allowed free

79

access to drinking water and diet. The animals were acclimatized to the facilities for a

80

week, and then fasted with free access to water for 12 h prior to experiment.

81

Animals were divided into ten groups randomly, and each group had six rats.

82

Two groups were kept in regular cages and treated with 400 mg/kg body weight of

5

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

83

3-MCPD 1-monopalmitate or pure olive oil vehicle, and 300 µL of blood sample was

84

collected in heparinized eppendorf tube via the oculi chorioideae vein before dosing

85

and subsequently at 0, 0.167, 0.33, 0.5, 0.75, 1, 1.5, 2, 2.5, 3, 4, 6, 8, 12, and 24 h

86

after the treatment for the kinetic study. Another four groups were kept in metabolic

87

cages, treated with 400 mg/kg body weight of 3-MCPD 1-monopalmitate, and

88

sacrificed to collect the liver, kidney, testis, brain, plasma and urine samples at 6, 12,

89

24 and 48 hours after treatment. The four control groups were sacrificed at 6, 12, 24

90

and 48 hours after oral administration of same volume pure olive oil. Water and food

91

were fed ad libitum 4 hours after treatment during the experiment.

92

Animal samples. The blood samples were centrifuged at 4000 rpm for 10

93

minutes at 4 °C, and 100 µL of supernatant plasma was accurately collected and

94

immediately frozen at -80 °C until further analysis. 300 µL of acetonitrile was added

95

to each 100 µL of the plasma sample. The mixture was vortexed for 30 s, and

96

followed by centrifugation at 10000 rpm for 10 minutes at 4 °C. The supernatant was

97

transferred into a UPLC vial for UPLC-QQQ-MS analysis.

98

The liver, kidney, testis and brain samples were removed, weighed, flushed in

99

ice-cold saline (0.9% NaCl), and homogenized at 4 °C in 9 times weight ice-cold

100

saline to make 10% tissue homogenate. The homogenate was stored at -80 °C, and

101

centrifuged at 10000 rpm at 4 °C for 10 min to obtain the supernatant for

102

UPLC-Q-TOF-MS analysis.

103

Page 6 of 28

The urine samples were collected in metabolic cages at different time points. For

6

ACS Paragon Plus Environment

Page 7 of 28

Journal of Agricultural and Food Chemistry

104

example, urine samples at 12 hour indicated the urine collected between 6 hour and

105

12 hour. 0.2 mL of each urine sample was extracted with 1 mL of water-saturated

106

ethyl acetate by vortexing for 30 s and followed by centrifugation at 10000 rpm for 10

107

min at ambient temperature. The supernatant was transferred into a clean tube and the

108

solvent was removed using a nitrogen evaporator. The residue was re-dissolved in 0.2

109

mL of methanol and subjected to UPLC-Q-TOF-MS analysis.

110 111

UPLC-MS conditions. A Waters Acuity UPLC-TQS triple quadrupole MS

112

system (Waters, Milford, MA, USA) was selected for quantitatively analysis of

113

3-MCPD 1-monopalmitate in rat plasma samples with a Waters Phenyl column (2.1

114

mm i.d. × 100 mm, 1.7 µm). The mobile phase consisted of A) water/methanol (9:1,

115

v/v) and B) methanol/ isopropanol (4:1, v/v) using the elution gradient started with 0%

116

phase B, changed linearly to 35% in 4 min, increased linearly to 95% B at 8 min and

117

maintained for 2 min, and returned to its initial condition for 2 min to re-equilibrate

118

the column for the next injection. The flow rate was 0.4 mL/min with an injection

119

volume of 2 µL. The MS detector conditions were: capillary voltage 3.50 kV;

120

sampling cone voltage 60 V; extraction cone voltage 4.0 V; source temperature

121

120 °C; and desolvation temperature 450 °C. The flow rates were 150 L/h for cone

122

gas and were 800 L/h for the desolvation gas. An ion pair with a parent ion at m/z

123

371.2329 ([M+Na]+) and a daughter ion at m/z 110.0135 was selected to create a

124

multiple reaction monitoring (MRM) system with the collision energy of 35 eV and a

7

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

125 126

Page 8 of 28

mass range from 50 to 1000 m/z in an ESI positive mode. A Waters Acuity UPLC-Xevo G2 Q-TOF MS system (Waters, Milford, MA,

127

USA) was selected for metabolite identification and relatively quantification in this

128

study. UPLC condition was almost similar as UPLC QQQ MS. Briefly, a Waters

129

Phenyl column (2.1 mm i.d. × 100 mm, 1.7 µm) was utilized with a Waters Acuity

130

UPLC-Xevo G2 quadrupole-time of flight mass spectrometry (Q-TOF MS). The

131

mobile phase consisted of A) water/methanol (9:1, v/v) and B) methanol/ isopropanol

132

(4:1, v/v) using the elution gradient started with 0% phase B, changed linearly to 35%

133

in 4 min, increased linearly to 95% B at 8 min and maintained for 2 min, and returned

134

to its initial condition for 2 min to re-equilibrate the column for the next injection.

135

The flow rate was 0.4 mL/min with an injection volume of 2 µL. The MS detector

136

conditions were: capillary voltage 3.00 kV; sampling cone voltage 60 V; extraction

137

cone voltage 4.0 V; source temperature 120 °C; and desolvation temperature 450 °C.

138

The cone gas flow rate was 150 L/h and the desolvation gas flow was 800 L/h. A MSE

139

method was used with mass range from 50 to 1200 m/z in both ESI positive and

140

negative modes, with a scan time of 0.3 s and the ramp collision energy at 20-35 eV.

141

Method evaluation. Different mobile phases, including different ratios of

142

methanol/water, acetonitrile/water and methanol/acetonitrile/isopropanol/water, were

143

tested in the preliminary study to select an appropriate mobile phase. Finally, mobile

144

phase with A) water/methanol (9:1, v/v) and B) methanol/isopropanol (4:1, v/v) with

145

gradient elution was utilized in this study. The limit of detection (LOD) and limit of

8

ACS Paragon Plus Environment

Page 9 of 28

Journal of Agricultural and Food Chemistry

146

quantification (LOQ) were tested by adding different concentrations of 3-MCPD

147

1-monopalmitate into blank rat plasma samples. The LOD was determined in the

148

relative standard deviation (RSD) less than 20% and accuracy (average concentration

149

deviated from the formulated concentration) to less than ± 20% of the measured

150

results. Every sample was tested in triplicate. The LOQ was determined in the

151

signal/noise (S/N) = 10, and the LOQ in this study was 2 ng/mL of 3-MCPD

152

1-monopalmitate. The standard curve showed linear range between 10 to 1000 ng/mL

153

determined by 7 different concentrations of 3-MCPD 1-palmitate with a r2 value of

154

0.998.

155

Recovery was determined by adding low (30 ng/mL), medium (300 ng/mL) and

156

high (1000 ng/mL) concentrations of 3-MCPD 1-monopalmitate into blank rats’

157

plasma samples, and prepared them following the same protocol for quantification.

158

Each concentration was examined in triplicate. The results indicated that the recovery

159

of 3-MCPD 1-monopalmitate in plasma samples was 82.55 to 104.63%.

160

Kinetic data analysis and statistical evaluation. Pharmacokinetic analysis was

161

performed using 3P97® software (Practical Pharmacokinetic Program, Beijing, China).

162

Several kinetic parameters such as the maximum concentration (Cmax), time to

163

maximum concentration (tmax), mean residence time (MRT), and area under the

164

concentration–time curve (AUC) was determined. Cmax and tmax were obtained

165

directly from the plasma concentration–time data and AUC was calculated by the

166

trapezoidal rule.

9

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 10 of 28

167

Results were expressed as mean ± standard deviation (S.D.). Statistics were

168

analyzed using the SPSS for Windows (version rel. 10.0.5, 1999, SPSS Inc., Chicago,

169

IL).

170 171

Results and Discussion

172

Kinetics of 3-MCPD 1-monopalmitate in the plasma. The kinetics of

173

3-MCPD 1-monopalmitate in rat plasma after oral administration was evaluated for

174

the first time. The greatest concentration of 3-MCPD 1-monopalmitate in the plasma

175

was 873.72 ng/mL (Cmax) at about 1.67 hours (Tmax) after oral administration (Table

176

1), and no free 3-MCPD was detected in the plasma samples at any tested time points

177

under the experimental conditions. A previous study reported the existence of high

178

level of free 3-MCPD in the blood of Wistar rats using indirect GC-MS determination

179

of its heptafluorobutyric acid derivatives.20 Different results between this study and

180

the present study might because of different types and age of rats utilized in these two

181

studies, the amount of blood samples used to prepare the analytical samples, and the

182

limitation of detecting free 3-MCPD using LC-MS. Plasma 3-MCPD

183

1-monopalmitate concentration reduced to half after 3.42 hours (t1/2). No 3-MCPD

184

1-monopalmitate could be detected after 4 hours, which was its mean resident time

185

(MRT). The area under curve (AUC) for 3-MCPD 1-monopalmitate in rat plasma was

186

1676.15 h.ng/mL, which represented the maximum amount of 3-MCPD

187

1-monopalmitate absorbed into plasma under the testing conditions. These results

10

ACS Paragon Plus Environment

Page 11 of 28

Journal of Agricultural and Food Chemistry

188

indicated that 3-MCPD 1-monopalmitate could be absorbed and involved in body

189

circulation in vivo in its ester form, and could be eliminated from the circulation

190

system in 4 hours possibly through metabolism and/or elimination or tissue

191

distribution mechanisms. To the best of our knowledge, this is the first report on

192

3-MCPD 1-monopalmitate kinetics in an animal model.

193

3-MCPD 1-monopalmitate concentrations in rats’ organs and tissues. The

194

relative concentrations of 3-MCPD 1-monopalmitate in the liver, kidney, testis and

195

brain of rats were also evaluated at 6, 12, 24 and 48 hours after administration in this

196

study. Unfortunately the matrix effects of different organs and tissues made it difficult

197

to measure the concentration of 3-MCPD 1-monopalmitate in each organs and tissues

198

by UPLC QQQ-MS, and UPLC QTOF-MS was used. 3-MCPD 1-monopalmitate

199

could be detected only in the liver sample collected 6 h after administration, and the

200

average absolute peak area was 90.88. This observation could also be partially due to

201

the limitation in the quantitative resolution of UPLC QTOF-MS. All these data that

202

3-MCPD 1-monopalmitate was existed in vivo with its original form raised a question

203

whether and how 3-MCPD monoester might be delivered into and be metabolized

204

locally in each rat organ or tissue.

205

Identification of 3-MCPD 1-monopalmitate metabolites in rats’ tissues,

206

plasma and urine. Liver, kidney, testis and brain, as well as plasma and urine of rats

207

were collected at 6, 12, 24 and 48 hours after oral administration of 3-MCPD

208

1-monopalmitate. Liver is the most important metabolic organ, whereas kidney and

11

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 12 of 28

209

testis have been reported as the targets for the toxic effects of 3-MCPD esters.10, 21, 22

210

Brain was selected because the possible nerve toxicity of 3-MCPD esters observed in

211

our previous studies,10 and it is important to investigate whether original form or

212

metabolites of 3-MCPD 1-monopalmitate could pass through the blood-brain barrier.

213

Blood plasma is the most important body fluid and could reflect in vivo environment,

214

while urine is one of the most widely used biological samples in studying the

215

excretion of metabolites. Liver, kidney, testis, brain and blood were collected from the

216

sacrificed rats at the selected time points, while urine samples were collected using

217

the metabolic cage.

218

The metabolites were identified using UPLC Q-TOF MS and Waters Masslynx

219

4.1 and Waters MetaboLynx XS softwares. A total of 8 metabolites were tentatively

220

identified based on their accurate formula masses and fragment ion patterns. Major

221

metabolites including 3-MCPD, sulfonated 3-MCPD, acetylated 3-MCPD,

222

glucuronide 3-MCPD, and 3-MCPD bonded with different amino acids (Figure 1).

223

Besides, some metabolites were also detected and speculate as multi-hydroxylated

224

3-MCPD and methylated-hydroxylated 3-MCPD, and their structures were not

225

reported in the Figure 1.

226

The acetylated metabolite was selected as the example to demonstrate how those

227

metabolites were characterized. The total ion chromatography of a typical LC-MS

228

chromatography of a liver sample and the extracted ion chromatography of acetylated

229

metabolites were showed in Figure 2A and 2B, respectively. The MS1 (parent ion)

12

ACS Paragon Plus Environment

Page 13 of 28

Journal of Agricultural and Food Chemistry

230

and MS2 (fragment ion) mass spectra of the acetylated metabolite with a retention

231

time of 1.13 min (Figure 2B) were obtained (Figure 3A and 3B). In the MS1

232

spectrum, the molecular ion peak of the metabolite was 151.0258 [M-H]-, so the

233

molecular formula could be calculated as C5H9ClO3. In the MS2 spectrum, the major

234

fragment ion peak was 135.0306 [M-OH], combined with the information supplied

235

from MetaboLynx XS, the structure could be identified as the acetylated 3-MCPD, the

236

major peak at m/z 135.0306 in the MS2 could be the structure obtained by eliminating

237

a sn-2 hydroxyl group from 3-MCPD. It is understandable that the acetylation could

238

also be at the sn-2 position. The site for acetylation of 3-MCPD was finally proposed

239

as the sn-1 position due to the relatively lower steric hindrance of this structure.

240

A previous study reported that free 3-MCPD could be detected in the serum 30

241

min after oral administration of 3-MCPD esters to F344 rats.22 Glycidol was also

242

detected in rats serum after oral administration of either glycidol or 3-MCPD di-esters.

243

These two metabolites were not detected in plasma samples in this study at all tested

244

time points. Only trace amount of free 3-MCPD was detected in urine samples at 24

245

hours after oral administration of 3-MPCD 1-monopalmitate to SD rats. No glycidol

246

was detected in any tissue or urine samples in this study. In brief, this study

247

characterized 8 metabolites in rats’ tissues and/or plasma and urine samples after oral

248

administration of 3-MCPD 1-monopalmitate for the first time.

249

Tissue distribution of 3-MCPD 1-monopalmitate metabolites. After

250

tentatively identified the eight metabolites, the distribution of these metabolites in

13

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 14 of 28

251

different tissues and body fluids were examined. Acetylated 3-MCPD was detected in

252

liver, kidney, testis, urine and brain samples, but not in the plasma samples.

253

Glucuronide conjugated 3-MCPD was detected in urine and plasma samples. Free

254

3-MCPD, sulfate conjugated 3-MCPD and glycine conjugated 3-MCPD was only

255

detected in urine samples. Hydroxylated and glucuronide conjugated 3-MCPD,

256

cysteine conjugated 3-MCPD and taurine conjugated 3-MCPD was only detected in

257

plasma samples. Acetylated 3-MCPD is the most widely distributed metabolite in the

258

rats after oral administration 3-MCPD 1-monopalmitate. It presented in all the four

259

tested tissues, including liver, kidney, testis and brain, suggesting its potential to pass

260

through the blood-brain barrier. It was also detected in the urine samples, indicating

261

that this metabolite might be one excreting form of 3-MCPD 1-monopalmitate and

262

possibly other 3-MCPD esters. Glucuronide conjugated, sulfate conjugated, glycine

263

conjugated and free 3-MCPD was also detected in urine samples, and might be other

264

possible excreting forms for 3-MCPD 1-monopalmitate and other esters. Glucuronide

265

conjugated, hydroxylated and glucuronide conjugated, cysteine conjugated and

266

taurine conjugated 3-MCPD was detected in plasma, suggesting that glucuronide and

267

amino acid addition might be two important ways to distribute 3-MCPD

268

1-monopalmitate into blood (Figure 4).

269

In addition, the existences of these metabolites in the selected tissue and fluid

270

samples were also evaluated at different time points. Acetylated 3-MCPD was

271

detected at all the four time points (4, 12, 24 and 48 h) in liver and kidney samples,

14

ACS Paragon Plus Environment

Page 15 of 28

Journal of Agricultural and Food Chemistry

272

at 12 and 24 hours in the testis and urine samples after oral administration of 3-MCPD

273

1-monopalmitate, respectively. Free 3-MCPD, glycine conjugated and sulfate

274

conjugated 3-MCPD was only detected at 12-hour urine samples. Glucuronide

275

conjugated, hydroxylated and glucuronide conjugated and taurine conjugated

276

3-MCPD was detected in 6-hour plasma samples, whereas cysteine conjugated

277

3-MCPD presented in the plasma samples at all the four tested time points.

278

Possible metabolic pathway of 3-MCPD 1-monopalmitate in vivo. Based on

279

the information above, the possible metabolic pathway of 3-MCPD 1-monopalmitate

280

in vivo was proposed using MetaboLynx (Figure 4). Briefly, 3-MCPD

281

1-monopalmitate hydrolyzed and loss its fatty acid fragments to form the free

282

3-MCPD (phase I metabolite). After that, the free 3-MCPD combined with the

283

endogenous substances in vivo, increased polarity for easy urine excretion (phase II

284

metabolites). Sulfonated 3-MCPD, acetylated 3-MCPD, glucuronide 3-MCPD and all

285

the amino acid conjugated 3-MCPD are the typical phase II metabolites in vivo. This

286

pathway clearly represent the possible metabolic process of 3-MCPD

287

1-monopalmitate in vivo, especially the chlorine-contained fragment of 3-MCPD

288

ester distributed and excreted. 3-MCPD 1-monopalmit was same as common

289

glycerides and could be metabolized through acetylation, glucuronide and sulfonation,

290

but was unique to be able to form the three amino acid conjugated 3-MCPD. The

291

existence of these metabolites might because of the potential toxicity of 3-MCPD

292

1-monopalmitate induced more endogenous metabolic reactions to promote its

15

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

293 294

Page 16 of 28

excretion. In summary, this study represents the absorption, distribution, metabolism and

295

excretion of 3-MCPD 1-monopalmitate in rats. The toxicokinetic factors were

296

clarified, 8 chlorine-related metabolites were tentatively identified and relatively

297

quantified based on their peak areas in the major tissues, plasma and urine in four

298

different time points, and the major excretion form of 3-MCPD 1-monopalmitate was

299

also detected as its phase II metabolites. Besides, there are still large amount of

300

metabolites remain in tissues 48 hours after oral administration of 3-MCPD

301

1-monopalmitate to rats, such as the acetylated 3-MCPD in liver and kidney, and the

302

cysteine conjugated 3-MCPD in testis. Suppose that people consume foods contained

303

3-MCPD esters everyday, these metabolites might be accumulated in the

304

organs/tissues. Therefore, the toxicity effects of these metabolites should also be

305

investigated. The present study might advance our understanding of the metabolism

306

process of 3-MCPD esters and provide a base for further studies to have a better

307

understanding about the toxicity effects and mechanisms of 3-MCPD esters in vivo.

308 309

Funding

310

We gratefully acknowledge the financial support from a Special Fund for

311

Agro-scientific Research in the Public Interest (Grant No. 201203069), the National

312

High Technology Research and Development Program of China (Grant Nos.

313

2013AA102202; 2013AA102207), a Grant from the Wilmar (Shanghai)

16

ACS Paragon Plus Environment

Page 17 of 28

Journal of Agricultural and Food Chemistry

314

Biotechnology Research & Development Center Co. Ltd, and Shanghai Jiao Tong

315

University 985-III disciplines platform and talent funds (Grant Nos. TS0414115001;

316

TS0320215001).

17

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 18 of 28

317

References

318

1.

319

3-chloropropane-1,2-diol esters in models simulating processed foods. Czech J. Food

320

Sci. 2006, 24, 172-179.

321

2.

322

3-chloropropane-1,2-diol in edible oils. Food Addit. Contam. 2006, 23, 1290-1298.

323

3.

324

coffee surrogates and malts. Czech J. Food Sci. 2007, 25, 39-47.

325

4.

326

Esters of 3-chloro-1,2-propanediol (3-MCPD) in vegetable oils: significance in the

327

formation of 3-MCPD. Food Addit. Contam. Part A Chem. Anal. Control Expo. Risk

328

Assess. 2008, 25, 391-400.

329

5.

330

problem. Eur. J. Lipid Sci. Tech. 2008, 110, 671-672.

331

6.

332

fatty acid esters in infant and baby foods. Eur. Food Res. Technol. 2009, 228,

333

571-578.

334

7.

335

Occurrence of 3-MCPD fatty acid esters in human breast milk. Food Addit. Contam.

336

Part A Chem. Anal. Control Expo. Risk Assess. 2008, 25, 669-676.

337

8.

Svejkovska, B.; Dolezal, M.; Velisek, J. Formation and decomposition of

Zelinková, Z.; Svejkovská, B.; Velísek, J.; Dolezal, M. Fatty acid esters of

Divinova, V.; Dolezal, M.; Velisek, J. Free and bound 3-chloropropane-1,2-diol in

Seefelder, W.; Varga, N.; Studer, A.; Williamson, G.; Scanlan, F. P.; Stadler, R. H.

Weisshaar, R. 3-MCPD-esters in edible fats and oils - a new and worldwide

Zelinkova, Z.; Dolezal, M.; Velisek, J. Occurrence of 3-chloropropane-1,2-diol

Zelinkova, Z.; Novotny, O.; Schurek, J.; Velisek, J.; Hajslova, J.; Dolezal, M.

Svejkovska, B.; Novotny, O.; Divinova, V.; Reblova, Z.; Dolezal, M.; Velisek, J.

18

ACS Paragon Plus Environment

Page 19 of 28

Journal of Agricultural and Food Chemistry

338

Esters of 3-chloropropane-1,2-diol in foodstuffs. Czech J. Food Sci. 2004, 22,

339

190-196.

340

9.

341

3-monochloropropane-1,2-diol (3-MCPD) in food in Europe in the years 2009-2011

342

and preliminary exposure assessment. EFSA J. 2013, 11, 3381-3345.

343

10. Liu, M.; Gao, B.; Qin, F.; Wu, P.; Shi, H.; Luo, W.; Ma, A.; Jiang, Y.; Xu, X.; Yu,

344

L. Acute oral toxicity of 3-MCPD mono- and di-palmitic esters in Swiss mice and

345

their cytotoxicity in NRK-52E rat kidney cells. Food Chem. Toxicol. 2012, 50,

346

3785-3791.

347

11. Zhang, X.; Gao, B.; Qin, F.; Shi, H.; Jiang, Y.; Xu, X.; Yu, L. Free Radical

348

Mediated Formation of 3-Monochloropropanediol (3-MCPD) Fatty Acid Diesters. J.

349

Agric. Food Chem. 2013, 61, 2548-2555.

350

12. Zhang, Z.; Gao, B.; Zhang, X.; Jiang, Y.; Xu, X.; Yu, L. Formation of

351

3-monochloro-1,2-propanediol (3-MCPD) di- and monoesters from tristearoylglycerol

352

(TSG) and the potential catalytic effect of Fe²+ and Fe³+. J Agric. Food Chem. 2015,

353

63, 1839-1848.

354

13. Liu, M.; Huang, G.; Wang, T. T.; Sun, X.; Yu, L. 3-MCPD 1-Palmitate Induced

355

Tubular Cell Apoptosis In Vivo via JNK/p53 Pathways. Toxicol. Sci. 2016, 151,

356

181-192.

357

14. Sawada, S.; Oberemm, A.; Buhrke, T.; Meckert, C.; Rozycki, C.; Braeuning, A.;

358

Lampen, A. Proteomic analysis of 3-MCPD and 3-MCPD dipalmitate toxicity in rat

Europen Food Safety Authority. Analysis of occurrence of

19

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 20 of 28

359

testis. Food Chem. Toxicol. 2015, 83, 84-92.

360

15. Onami, S.; Cho, Y. M.; Toyoda, T.; Mizuta, Y.; Yoshida, M.; Nishikawa, A.;

361

Ogawa, K. A 13-week repeated dose study of three 3-monochloropropane-1,2-diol

362

fatty acid esters in F344 rats. Arch. Toxicol. 2014, 88, 871-80.

363

16. Li, J.; Wang, S.; Wang, M.; Shi, W.; Du, X.; Sun, C. The toxicity of

364

3-chloropropane-1,2-dipalmitate in Wistar rats and a metabonomics analysis of rat

365

urine by ultra-performance liquid chromatography-mass spectrometry. Chem. Biol.

366

Interact. 2013, 206, 337-45.

367

17. Buhrke, T.; Frenzel, F.; Kuhlmann, J.; Lampen, A. 2-Chloro-1,3-propanediol

368

(2-MCPD) and its fatty acid esters: cytotoxicity, metabolism, and transport by human

369

intestinal Caco-2 cells. Arch. Toxicol. 2015, 89, 2243-2251.

370

18. Andreoli, R.; Cirlini, M.; Mutti, A. Quantification of 3-MCPD and its

371

mercapturic metabolite in human urine: validation of an LC-MS-MS method and its

372

application in the general population. Anal. Bioanal. Chem. 2015, 407, 4823-7.

373

19. Ji, J.; Zhang, L.; Zhang, H.; Sun, C.; Sun, J.; Jiang, H.; Abdalhai., M.H.; Zhang,

374

Y.; Sun, X. 1H NMR-based urine metabolomics for the evaluation of kidney injury in

375

Wistar rats by 3-MCPD. Toxicol. Res. 2016, 5, 689-696.

376

20. Abraham, K., Appel, K.E., Berger-Preiss, E., Apel, E., Gerling, S., Mielke, H.,

377

Creutzenberg, O., Lampen, A. Relative oral bioavailability of 3-MCPD from 3-MCPD

378

fatty acid esters in rats. Arch. Toxicol. 2013, 87, 649-659.

379

21. Onami, S.; Cho, Y. M.; Toyoda, T.; Horibata, K.; Ishii, Y.; Umemura, T.; Honma,

20

ACS Paragon Plus Environment

Page 21 of 28

Journal of Agricultural and Food Chemistry

380

M.; Nohmi, T.; Nishikawa, A.; Ogawa, K. Absence of in vivo genotoxicity of

381

3-monochloropropane-1,2-diol and associated fatty acid esters in a 4-week

382

comprehensive toxicity study using F344 gpt delta rats. Mutagenesis. 2014, 29,

383

295-302.

384

22. Onami, S.; Cho, Y. M.; Toyoda, T.; Akagi, J.; Fujiwara, S.; Ochiai, R.; Tsujino, K.;

385

Nishikawa, A.; Ogawa, K., Orally administered glycidol and its fatty acid esters as

386

well as 3-MCPD fatty acid esters are metabolized to 3-MCPD in the F344 rat. Regul.

387

Toxicol. Pharmacol. 2015, 73, 726-31.

388

21

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 22 of 28

Table 1. Absorption of 3-MCPD 1-monopalmitate in Rats Animal ID 1

2

3

4

5

6

mean

sd

Cmax a

ng/mL

814.74

887.47

680.83

752.69

988.05

1118.55

873.72

160.33

Tmax b

h

2.50

1.50

1.50

1.50

1.50

1.50

1.67

0.41

h

3.50

3.50

4.00

3.00

3.50

3.00

3.42

0.38

h

4.00

4.00

4.00

4.00

4.00

4.00

4.00

0.00

h.ng/mL

2119.80

2000.66

1201.04

1433.48

1472.26

1829.66

1676.15

361.08

t1/2

c

MRT

d

AUC 0-∞ a

e

Cmax is the maximum concentration of 3-MCPD 1-monopalmitate in rats’ plasma; b Tmax is the time of reach the Cmax after oral administration to rats; c t1/2 is the time that the

concentration of 3-MCPD 1-monopalmitate reduced to half of Cmax; d MRT is the abbreviation of mean residence time, indicate the average time of 3-MCPD 1-monopalmitate stays in the body; e AUC is the abbreviation of area under the curve, represent the total amount of 3-MCPD 1-monopalmitate stay in the body.

22

ACS Paragon Plus Environment

Page 23 of 28

Journal of Agricultural and Food Chemistry

Figure Captions Figure 1. Chemical structures of metabolites. Figure 2. Typical UPLC-QTOF-MS A) total ion chromatogram (TIC) of rat liver sample extracts and B) extract ion chromatogram for the acetylated metabolite after oral administration of 3-MCPD 1-monopalmitate to rats. Figure 3. MS spectra of the acetylated metabolite. A) MS1 spectrum and B) MS2 spectrum. Figure 4. Possible metabolic pathway of 3-MCPD 1-monopalmitate in rats.

23

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 24 of 28

Figure 1.

24

ACS Paragon Plus Environment

Page 25 of 28

Journal of Agricultural and Food Chemistry

A)

B)

Figure 2.

25

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 26 of 28

A)

B)

Figure 3.

26

ACS Paragon Plus Environment

Page 27 of 28

Journal of Agricultural and Food Chemistry

Figure 4.

27

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 28 of 28

TOC Graphic

28

ACS Paragon Plus Environment