Comparative Toxicokinetics, Absolute Oral ... - ACS Publications

May 7, 2015 - Department of Veterinary Public Health and Food Safety, Faculty of ..... high Vd value is observed after PO and IV administration in all...
0 downloads 0 Views 485KB Size
Subscriber access provided by NATIONAL CENTRAL UNIV

Article

Comparative toxicokinetics, absolute oral bioavailability and biotransformation of zearalenone in different poultry species Mathias Devreese, Gunther Antonissen, N. Broekaert, Siegrid De Baere , Lynn Vanhaecke, Patrick De Backer, and Siska Croubels J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.5b01608 • Publication Date (Web): 07 May 2015 Downloaded from http://pubs.acs.org on May 10, 2015

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 32

Journal of Agricultural and Food Chemistry

Comparative toxicokinetics, absolute oral bioavailability and biotransformation of zearalenone in different poultry species Mathias Devreese*1, Gunther Antonissen1,2, Nathan Broekaert1, Siegrid De Baere1, Lynn Vanhaecke³, Patrick De Backer1, Siska Croubels1 1

Department of Pharmacology, Toxicology and Biochemistry, Faculty of Veterinary Medicine, Ghent University, Salisburylaan 133, B-9820 Merelbeke

² Department of Pathology, Bacteriology and Avian Diseases, Faculty of Veterinary Medicine, Ghent University, Salisburylaan 133, B-9820 Merelbeke ³ Department of Veterinary Public Health and Food Safety, Faculty of Veterinary Medicine, Ghent University, Salisburylaan 133, B-9820 Merelbeke E-mail addresses: [email protected]; [email protected]; [email protected]; [email protected]; [email protected]; [email protected]; [email protected] *Corresponding Author: E-mail address: [email protected], Tel: + 32 9 264 73 24, Fax: +32 9 264 74 97

1 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 2 of 32

1

Abstract – After oral (PO) and intravenous (IV) administration of zearalenone (ZEN) to broiler

2

chickens, laying hens and turkey poults, the mycotoxin was rapidly absorbed (Tmax = 0.32 –

3

0.97 h) in all three species, however, the absolute oral bioavailability was low (F% = 6.87 –

4

10.28%). Next, also a rapid elimination of the mycotoxin in all poultry species was observed

5

(T1/2el = 0.29 – 0.46 h). Both α- and β-zearalenone (ZEL) were formed equally after IV

6

administration in all species studied, whereas an increased biotransformation to β-ZEL was

7

demonstrated after PO administration indicating pre-systemic biotransformation mainly in

8

broiler chickens and laying hens. In comparison to the latter, turkey poults demonstrated a

9

more extensive biotransformation of ZEN to α-ZEL after PO administration which could, in

10

combination with the observed higher volume of distribution of ZEN, indicate a higher

11

sensitivity of this species to the effects of ZEN in comparison to other poultry species.

12

13

Keywords – poultry; laying hen; turkey; broiler chicken; zearalenone; toxicokinetics;

14

biotransformation

2 ACS Paragon Plus Environment

Page 3 of 32

Journal of Agricultural and Food Chemistry

15

Introduction

16

Mycotoxins are secondary metabolites produced by different fungal species contaminating

17

several food and feed commodities. Over 400 mycotoxins have been identified, although

18

only a few of them are known to have distinct toxic effects. The most prevalent mycotoxin

19

producing fungi in moderate climates are Fusarium species. Zearalenone (ZEN) is one of the

20

most frequently occurring Fusarium mycotoxins. In a recent study by Streit 1, 87% of the 83

21

investigated feed and feed raw material samples were contaminated with ZEN, with a

22

median contamination level of 14 µg/kg and a maximum of 5.3 mg/kg. ZEN can be listed as a

23

non-steroidal estrogen or myco-estrogen 2. It resembles 17β-estradiol, the principal

24

hormone produced by the ovary, which allows ZEN to bind to estrogen receptors in target

25

cells 3. Once the estrogen receptor is bound, it undergoes a conformational change allowing

26

the receptor to interact with chromatin and to modulate transcription of target genes 4. Not

27

all compounds have the same affinity for estrogen receptors. It has been shown that some

28

phase I metabolites of ZEN can express lower or even higher affinities to estrogen receptors

29

than the parent compound. In general, ZEN is metabolized by 3α- and 3β-hydroxysteroid

30

dehydrogenase (HSD) into α- and β-zearalenol (ZEL), respectively. β-ZEL has a 2.5 times

31

lower affinity for the estrogen receptor, whereas α-ZEL has a 92 times higher binding affinity

32

compared to ZEN. The biotransformation to β-ZEL can therefore be regarded as an

33

inactivation pathway, whereas the biotransformation to α-ZEL can be seen as a bio-

34

activation5. The rate and extent of α- or β-ZEL production, and consequently the

35

susceptibility, is species dependent. Pigs are regarded as the most sensitive species, as

36

suggested by in vitro data demonstrating that pig liver microsomes dominantly convert ZEN

37

into α-ZEL 5. This has been confirmed in vivo where α-ZEL was the only phase I metabolite

38

detected in plasma, urine and faeces of pigs intravenously (IV) dosed with ZEN 6. Next, in a 3 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

7

Page 4 of 32

39

study by Zöllner

the α-ZEL/β-ZEL ratios were 2.5/1 and 3/1 in pig liver and urine,

40

respectively, after oral intake of ZEN. In vitro results suggest that laying hens and cattle

41

metabolize ZEN to a large extent into β-ZEL, which confirms that they are less prone to the

42

effects of ZEN

43

detoxification pathway. The extent of conjugation has also been found to have major inter-

44

species variation. Migdalof

45

the total ZEN recovered in humans, whereas in dogs glucuronidation only accounts for 1% of

46

the excreted ZEN metabolites.

47

To date, no in vivo data are available in poultry regarding the phase I and phase II

48

biotransformation of ZEN after oral exposure, which is mandatory to confirm the in vitro

49

findings and the species dependent sensitivity. Also, limited information on in vivo

50

toxicokinetics and absolute oral bioavailability is available. Osselaere

51

elimination of ZEN after IV administration of 0.3 mg ZEN/kg body weight (BW) to broiler

52

chickens (T1/2el = 0.53 h), whereas after oral (PO) administration of the same dose, no ZEN or

53

phase I metabolites could be detected in plasma (limit of quantification: 1-5 ng/mL). The

54

rapid elimination and the assumed low oral bioavailability of the mycotoxin supports the

55

limited toxicity of ZEN in this animal species. Furthermore, Dailey11 administered 10 mg

56

[14C]ZEN/kg BW to laying hens and demonstrated that 94% of the administered dose was

57

eliminated via the excreta within 72 h, with one-third as unchanged [14C]ZEN and the other

58

part as unidentified metabolites. Feeding mature laying hens a diet contaminated with ZEN

59

up to 800 mg/kg did not affect their reproductive performance 12, 13. In contrast, feeding 100

60

mg ZEN/kg feed to mature female turkeys, reduced the egg production by 20%

61

feeding 800 mg ZEN/kg feed to male turkeys for 2 weeks induced strutting behavior and an

62

increased size and coloration of caruncles and dewlaps, which was not present in birds fed

5, 8

. Next, also phase II biotransformation (conjugation) is regarded as a

9

reported that glucuronidated metabolites account for 99% of

10

reported a rapid

14

. Next,

4 ACS Paragon Plus Environment

Page 5 of 32

Journal of Agricultural and Food Chemistry

15

63

the uncontaminated diet

64

turkey poults is most probably attributed to differences in toxicokinetics and/or

65

biotransformation processes.

66

Therefore, the aim of the present study was to unravel the toxicokinetic behavior, absolute

67

oral bioavailability and biotransformation of ZEN after PO as well as IV administration in the

68

economically most important poultry species, namely broiler chickens, laying hens and

69

turkey poults.

70

Materials and Methods

71

Chemicals, products and reagents

72

The analytical standard of ZEN, used for both plasma analysis and the animal experiment

73

was obtained from Fermentek (Jerusalem, Israel). The analytical standards of α-ZEL, β-ZEL, α-

74

zearalanol (α-ZAL), β-zearalanol (β-ZAL) and zearalanone (ZAN) used for the analytical

75

experiments were obtained from Sigma-Aldrich (Bornem, Belgium). The internal standard

76

(IS),

77

Austria). All analytical standards were stored at ≤ -15 °C. Working solutions of ZEN, the

78

described metabolites, and the IS were prepared by appropriate dilution of the stock

79

solutions with acetonitrile (ACN) and stored at 2-8 °C. Water, methanol (MeOH), ACN and

80

glacial acetic acid used for the plasma analysis were of LC-MS grade and obtained from

81

Biosolve (Valkenswaard, The Netherlands). Water and dimethylsulfoxide (DMSO) used for

82

the animal experiment were of analytical grade and obtained from Filterservice (Eupen,

83

Belgium). Millex®-GV PVDF filter units (0.22 µm) were obtained from Merck-Millipore

84

(Overijse, Belgium).

13

. This difference in sensitivity between broiler chickens and

C18-ZEN, used for the analytical experiments was obtained from Romer Labs (Tulln,

5 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 6 of 32

85

Animals and experimental procedure

86

Six turkey Hybrid Converter poults (3 ♂ / 3 ♀, 0.95 ± 0.06 kg BW), broiler chickens (Ross 308,

87

3 ♂ / 3 ♀, 1.05 ± 0.05 kg BW) and laying hens (Brown Leghorn, 6 ♀, 1.04 ± 0.05 kg BW) were

88

obtained from a commercial breeder. During the experiment, animals were housed in group

89

and a 16 h light / 8 h dark light cycle was applied. Feed and water were given ad libitum

90

throughout the one week acclimatization period. Subsequently, twelve hours before the

91

start of the experiment, the animals were deprived of feed. After this period, three birds per

92

species were administered ZEN (3 mg/kg BW) by oral gavage (PO) whereas the other 3

93

birds/species were injected the same dose of ZEN in the wing vein (IV). The PO and IV bolus

94

solution was prepared by dissolving the ZEN standard in DMSO (10 mg/mL) and further

95

diluted with water (PO) or physiological saline (IV) up to a volume of 1 mL. Following

96

administration of the mycotoxin, 0.5 mL of blood was drawn from the leg vein at various

97

time points: 0 (just before administration) and 2, 5, 10, 20, 30, 40, 50, 60, 120, 180 and 240

98

min post-administration. Samples were centrifuged (2851 x g, 10 min, 4 °C) and aliquots of

99

plasma (150 µL) were stored at ≤ -15 °C until analysis. After a two-day wash-out period, the

100

protocol was repeated in a two-way cross-over design. The birds that received an IV injection

101

of the mycotoxin then received a PO bolus and vice versa. The dosing, blood collection and

102

sample storage was performed in the same way as the first administration. The animal

103

experiment was approved by the Ethical Committee of the Faculty of Veterinary Medicine

104

and Bioscience Engineering of Ghent University (EC 2014/118).

105

LC-MS/MS analysis

106

Sample treatment and quantification of ZEN, and its phase I metabolites (α-ZEL, β-ZEL, α-

107

ZAL, β-ZAL and ZAN, see Supplementary Figure 1), in poultry plasma was performed as 6 ACS Paragon Plus Environment

Page 7 of 32

Journal of Agricultural and Food Chemistry

108

previously described by De Baere et al. (2012) with minor modifications. Briefly, 50 µL of IS

109

working solution (50 ng/mL) were added to 150 µL of plasma, followed by the addition of

110

ACN up to 1 mL. Next, the sample was vortex mixed (15 sec) and centrifuged (8517 x g, 10

111

min, 4 °C). The supernatant was evaporated to dryness using nitrogen (N2, 45 ± 5 °C). The dry

112

residue was reconstituted in 200 µL of water/MeOH (85/15, v/v), vortex mixed (15 sec),

113

filtered through a Millex® GV-PVDF syringe filter and transferred into a conical autosampler

114

vial. An aliquot (5 µL) was injected onto the LC-MS/MS instrument.

115

Chromatographic separation was achieved on a Hypersil® Gold column (50 mm x 2.1 mm i.d.,

116

dp: 1.9 µm) in combination with a guard column of the same type (10 mm x 2.1 mm i.d., dp:

117

3 µm), both from ThermoFisher Scientific (Breda, The Netherlands). Mobile phase A

118

consisted of 0.1% acetic acid in water whereas mobile phase B was ACN. Following gradient

119

elution program was run: 0-0.5 min (70% A, 30% B), 0.5-5.0 min (linear gradient to 70% B),

120

5.0-6.4 min (30% A, 70% B), 6.4-6.5 min (linear gradient to 30% B), 6.5-8.5 min (70% A, 30%

121

B). Flow rate was set at 300 µL/min and the temperature of the column oven and

122

autosampler tray were set at 45 and 5 °C, respectively.

123

Detection was performed on a Waters Xevo® TQ-S triple quadrupole mass spectrometer by

124

means of electrospray ionization (ESI) in the negative ionization mode. The instrument was

125

tuned by direct infusion of a 10 ng/mL working solution of ZEN, the metabolites and the IS.

126

The following parameters were retained for optimal detection: capillary voltage: 2.5 kV,

127

cone voltage: 15 V, source temperature: 150 °C, desolvation temperature: 600 °C, cone gas

128

flow: 150 L/h, desolvation gas flow: 1000 L/h. Acquisition was performed in the selected

129

reaction monitoring (SRM) mode. Following transitions (m/z) were used as quantifier and

130

qualifier ion, respectively, for ZEN: 317.1 > 175.0 and 317.1 >131.0, for α-ZEL: 319.0 > 275.0

7 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 8 of 32

131

and 319.0 > 159.9, for β-ZEL: 319.0 > 159.9 and 319.0 > 275.0, for ZAN: 319.0 > 205.0 and

132

319.0 > 275.0, for α-ZAL: 321.1 > 277.1 and 321.1 > 303.0, for β-ZAL: 321.1 > 277.1 and 321.1

133

> 303.0 and for the IS: 335.2 > 168.9 and 335.2 > 185.0. The method was validated for the

134

compounds listed above according to a validation protocol described by De Baere

135

on European

136

following parameters: linearity (correlation coefficient and goodness-of-fit), within- and

137

between-run accuracy and precision, carry-over, limit of quantification (LOQ) and limit of

138

detection (LOD). The LOQ was set at 0.5 ng/mL for ZEN, 0.2 ng/mL for α-ZEL and α-ZAL and

139

0.1 ng/mL for β-ZEL, β-ZAL and ZAN.

140

UHPLC-HRMS analysis

141

The extracted samples were also analyzed by UHPLC coupled to HRMS analysis for

142

identification and semi-quantification of the glucuronide conjugates of ZEN and of its phase I

143

metabolites as previously described by De Baere 19. This was performed based on the peak

144

area ratios of the metabolites, versus the IS. The UHPLC system consisted of an Accela® type

145

1250 High Speed LC and autosampler both from ThermoFisher Scientific. The same HPLC

146

column and mobile phases were used as described above. The UHPLC was interfaced to an

147

Exactive Orbitrap® HR mass spectrometer, equipped with a heated ESI probe operating in the

148

negative ionization mode (ThermoFisher Scientific). Accurate masses were based on the

149

predicted masses (m/z; [M-H]-) described by De Baere 19 and Stevenson 20: ZEN-glucuronide

150

(ZEN-GlcA, C24H30O11): 493.17153; ZAN-GlcA, α-ZEL-GlcA and β-ZEL-GlcA (C24H32O11, no

151

chromatographic separation or distinction between these compounds based on accurate

152

masses possible): 495.18718; α-ZAL-GlcA, β-ZAL-GlcA (C24H34O11, no chromatographic

153

separation or distinction between these compounds based on accurate masses possible):

17

and international

18

16

based

guidelines. The validation protocol encompassed

8 ACS Paragon Plus Environment

Page 9 of 32

Journal of Agricultural and Food Chemistry

154

497.20283. Confirmation of the GlcA peaks observed in the extracted ion chromatogram

155

(EIC) was performed by comparing the theoretically calculated 13C/12C isotope ratios for the

156

[M-H]- ion with the corresponding isotope ratios detected in the analyzed samples, as

157

described by De Baere 19.

158

Toxicokinetic analysis

159

Non compartmental toxicokinetic analysis of ZEN, α- and β-ZEL was performed with

160

WinNonlin 6.3 (Pharsight, St-Louis, MI, USA). For ZEN, following toxicokinetic parameters

161

were calculated for IV and PO administration: maximal plasma concentration for PO (Cmax),

162

plasma concentration at time 0 for IV (C0), time to maximal plasma concentration (Tmax), area

163

under the plasma concentration-time curve from time 0 to 3 h (AUC0-t), area under the

164

plasma concentration-time curve from time 0 to infinite (AUC0-inf), elimination rate constant

165

(kel), elimination half-life (T1/2el), total body clearance (Cl), volume of distribution (Vd) and

166

mean residence time (MRT).

167

The absolute oral bioavailability (F, expressed as %, F%) for each individual bird was

168

calculated according to the formula:

169

F% = AUC0-inf PO / AUC0-inf IV x 100

170

The Cl and Vd after PO administration was calculated by multiplying the data generated by

171

the toxicokinetic software (i.e. Vd/F and Cl/F) by the F from each individual bird.

172

The mean absorption time (MAT) was calculated according to the formula:

173

174

MAT = MRTPO – MRTIV The absorption rate constant (ka) and absorption half-life (T1/2a) were derived from the MAT:

9 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

175

ka = MAT-1

176

T1/2a = 0.693 / ka

Page 10 of 32

177

For α- and β-ZEL, the Cmax, Tmax, AUC0-t (from time 0 to the last time point above the LOQ, i.e.

178

2 or 3 h) and AUC0-inf were determined after both IV and PO administration of ZEN. Next,

179

ZEL/ZEN ratios were calculated according to the formulas:

180

α-ZEL/ZEN = (AUC0-inf α-ZEL) / (AUC0-inf ZEN)

181

β-ZEL/ZEN = (AUC0-inf β-ZEL) / (AUC0-inf ZEN)

182

ZEL/ZEN = (AUC0-inf α-ZEL + AUC0-inf β-ZEL) / (AUC0-inf ZEN)

183

184

Finally, the α-ZEL/β-ZEL ratio was calculated according to the formula: α-ZEL/β-ZEL = (AUC0-inf α-ZEL) / (AUC0-inf β-ZEL)

185

Statistical analysis

186

All toxicokinetic parameters from each compound (ZEN, α- and β-ZEL) and each

187

administration route were compared between animal species using one-way analysis of

188

variance (ANOVA) (SPSS 21, IBM, USA). The level of significance was set at 0.05.

189

Results and Discussion

190

The goal of this study was to unravel the toxicokinetic behavior, absolute oral bioavailability

191

and biotransformation of ZEN in different poultry species in order to assess potential species

192

dependent sensitivity to this mycotoxin. During the animal experiment, no clinical symptoms

193

were observed after PO or IV administration of ZEN to the birds. Furthermore, no sex

194

differences in toxicokinetic parameters were observed for broiler chickens and turkey poults.

10 ACS Paragon Plus Environment

Page 11 of 32

Journal of Agricultural and Food Chemistry

195

In figure 1A, B and C, the plasma concentration-time profiles of ZEN, α- and β-ZEL after IV

196

and PO administration of ZEN to broiler chickens, laying hens and turkey poults are

197

presented, respectively. Only trace amounts of α- and β-ZAL and ZAN were detected but

198

none above the LOQ of 0.2, 0.1 and 0.1 ng/mL, respectively. As can be seen in these figures

199

and Table 1, ZEN is rapidly absorbed in all studied poultry species, namely broiler chickens

200

(Tmax = 0.35 h, MAT = 0.37 h), laying hens (Tmax = 0.32 h, MAT = 0.35 h) and turkey poults

201

(Tmax = 0.97 h, MAT = 0.44 h). However, the F% is low in all studied poultry species, 8.34%,

202

10.28% and 6.87%, in broiler chickens, laying hens and turkey poults, respectively. This might

203

indicate either a low extent of absorption and/or extensive pre-systemic biotransformation,

204

and attributes to the generally accepted high tolerance of poultry to ZEN since F is a

205

measurement for systemic exposure. Next to rapid absorption, the mycotoxin is rapidly

206

eliminated in all species as well with T1/2el between 0.34 – 0.36 h and 0.29 – 0.46 h after PO

207

and IV administration, respectively. Osselaere

208

administration of 0.3 mg ZEN/kg BW to broiler chickens. Furthermore, a high Vd is observed

209

after PO and IV administration in all animal species (Vd = 3.21 – 10.65 L/kg). For broiler

210

chickens, an even higher Vd has been reported previously by Osselaere

211

L/kg, however this value was reported with a high uncertainty (15.15 L/kg). Of interest here

212

is that turkey poults have a significant higher Vd (9.03 – 10.65 L/kg) compared to broiler

213

chickens (3.21 – 4.16 L/kg) and laying hens (6.18 – 6.24 L/kg) which supports the hypothesis

214

of a higher sensitivity to ZEN of this species. Furthermore, the higher Vd explains why the C0

215

is significantly lower in turkey poults (C0 = 700.5 ng/mL) compared to broiler chickens (C0 =

216

2607.0 ng/mL) and laying hens (C0 = 2789.2 ng/mL) although they were administered the

217

same dose of ZEN (3 mg/kg BW). Also pigs display a high Vd of ZEN, comparable to turkey

218

poults, after IV administration, namely 10.84 L/kg, leading to a high tissue distribution of the

10

reported a similar T1/2el of 0.53 h after IV

10

, namely 22.26

11 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 12 of 32

219

mycotoxin 6. Besides a higher Vd in turkey poults, also a significantly higher Cl in turkeys (Cl =

220

16.57 – 19.66 L/h/kg) compared to broiler chickens (Cl = 9.06 – 11.1 L/h/kg) and laying hens

221

(Cl = 9.39 – 11.38 L/h/kg) was noticed. Since both Vd and Cl are higher in turkey poults, this

222

leads to a comparable T1/2el between the latter (T1/2el = 0.35 – 0.38 h) and broiler chickens

223

(T1/2el = 0.29 – 0.34 h) and laying hens (T1/2el = 0.36 – 0.46 h). Next, due to the higher Cl in

224

turkey poults and comparable F, the AUC0-inf is significantly lower in this species after both

225

administration routes (AUC0-inf PO = 10.21 h.ng/mL, AUC0-inf IV = 183.12 h.ng/mL) compared to

226

broiler chickens (AUC0-inf PO = 23.59 h.ng/mL, AUC0-inf IV = 292.10 h.ng/mL) and laying hens

227

(AUC0-inf PO = 30.04 h.ng/mL, AUC0-inf IV = 324.93 h.ng/mL). Similarly, also the AUC0-t was

228

significantly lower.

229

As described above, species dependent biotransformation of ZEN has a distinct impact on

230

sensitivity to this mycotoxin, and the in vitro estrogenic potency of its phase I metabolites is

231

as follows: α-ZAL > α-ZEL > β-ZAL > ZEN > β-ZEL 21. Phase I biotransformation of ZEN consists

232

of reduction of the ketone group of ZEN to its corresponding alcohol by 3α-/3β-HSD, thereby

233

forming α/β-ZEL, and aromatic hydrogenation of α/β-ZEL to α/β-ZAL by cytochrome P450

234

(CYP450) enzymes. Finally, α/β-ZAL can be oxidized by 3α-/3β-HSD to ZAN. The

235

biotransformation of ZEL to ZAL and ZAN has been reported for pigs and humans, however,

236

the extent is negligible 21. Also in the present study only trace amounts of α/β-ZAL and ZAN

237

were detected demonstrating that formation of α- and β-ZEL is also the predominant phase I

238

biotransformation in poultry. In all three poultry species both α- and β-ZEL could be detected

239

although the extent differed between species and routes of administration (Figure 1 and

240

Table 2). Turkey poults have a more efficient biotransformation of ZEN to α- and β-ZEL

241

compared to broiler chickens and laying hens, with higher α-ZEL/ZEN and β-ZEL/ZEN ratios

242

after both PO and IV administration (although not significant for β-ZEL/ZEN after PO), 12 ACS Paragon Plus Environment

Page 13 of 32

Journal of Agricultural and Food Chemistry

243

whereas these ratios are comparable between broiler chickens and laying hens (Table 2).

244

Consequently, also the ZEL/ZEN ratio in turkey poults is significantly higher after PO

245

(ZEL/ZENPO = 5.226) as well as IV administration (ZEL/ZENIV = 0.152) compared to broiler

246

chickens (ZEL/ZENPO = 1.149, ZEL/ZENIV = 0.032) and laying hens (ZEL/ZENPO = 2.086,

247

ZEL/ZENIV = 0.042). Furthermore, the biotransformation of ZEN to α- and β-ZEL occurs to a

248

greater extent after PO than after IV administration in all animal species. This difference in

249

ZEL formation between both administration routes indicates pre-systemic biotransformation

250

of ZEN in the gut and/or the liver. After IV administration, the α-ZEL/β-ZEL ratio is not

251

statistically different between bird species and is around 1 (α-ZEL/β-ZELIV = 1.073 to 1.629).

252

In contrast, after PO administration the β-ZEL isomer is predominantly formed in broiler

253

chickens (α-ZEL/β-ZELPO = 0.153) and laying hens (α-ZEL/β-ZELPO = 0.027), but this is

254

significantly different in turkey poults (α-ZEL/β-ZELPO = 0.749). Again, this indicates pre-

255

systemic formation of mainly β-ZEL, especially in broiler chickens and laying hens. These data

256

confirm the in vitro findings in laying hens, namely a predominant β-ZEL formation 5. Since

257

the α-ZEL/ZEN ratio after PO and IV ZEN administration is significantly higher in turkey poults

258

compared to both other bird species, this supports the hypothesis of increased sensitivity of

259

turkey poults to the estrogenic effects of the mycotoxin.

260

Phase II biotransformation of ZEN and its phase I metabolites comprises glucuronidation

261

which is catalyzed by uridine 5’-diphosphate glucuronosyltransferase (UGT)

262

analytical standards of glucuronidated ZEN (ZEN-GlcA) nor glucuronidated α- or β-ZEL (ZEL-

263

GlcA) are commercially available, no accurate quantitative analysis could be performed.

264

However, a semi-quantitative using HR-MS was done (Figure 2). After IV administration of

265

ZEN, ZEN-GlcA is the predominant phase II metabolite in all three bird species. Although the

266

ZEL/ZEN ratio is higher in turkey poults, namely 0.152, compared to broiler chickens and

22

. Since no

13 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 14 of 32

267

laying hens, 0.032 and 0.042 respectively, no ZEL-GlcA could be detected in this species after

268

IV administration, which is in contrast to the other species. After oral ZEN administration, a

269

comparable amount of ZEN-GlcA and ZEL-GlcA was detected in broiler chickens and laying

270

hens, whereas in turkey poults only ZEL-GlcA was detected, attributed to the high ZEL/ZEN

271

ratio in this species after PO administration (ZEL/ZEN = 5.226). This confirms the phase I

272

biotransformation data, namely a pre-systemic ZEL formation and consequent predominant

273

ZEL glucuronidation. Differences in phase II biotransformation might also account for

274

differences in sensitivity. For the mycotoxin DON, for instance, limited sulfation was

275

described for turkeys in contrast to broiler chickens, which might explain the increased

276

sensitivity of turkeys to deoxynivalenol

277

turkeys are more sensitive compared to other poultry and animal species based on

278

differences in biotransformation of AFB1. In turkeys, the phase I bio-activation of AFB1 to

279

AFB1-8,9-epoxide, is highly efficient and the epoxide metabolite is held responsible for the

280

hepatotoxic and carcinogenic effects of AFB1 24. Furthermore, turkeys have a glutathione-S-

281

transferase deficiency (phase II biotransformation) which adds to the sensitivity of this

282

species 25.

283

In conclusion, this paper describes – for the first time – the toxicokinetic behavior, absolute

284

oral bioavailability and comparative phase I and II biotransformation of ZEN in broiler

285

chickens, laying hens and turkey poults. ZEN is rapidly absorbed in all studied poultry

286

species, but the absolute oral bioavailability of the mycotoxin is low. Furthermore, it is

287

rapidly eliminated as well after both PO and IV administration. Both α- and β-ZEL were

288

formed equally after IV administration in all bird species, whereas an increased

289

biotransformation to β-ZEL was demonstrated after oral administration indicating pre-

290

systemic biotransformation processes, primarily in broiler chickens and laying hens. Finally,

23

. Also for the mycotoxin aflatoxin B1 (AFB1),

14 ACS Paragon Plus Environment

Page 15 of 32

Journal of Agricultural and Food Chemistry

291

the presented data suggest that turkey poults might be more sensitive to the effects of ZEN

292

based on the higher Vd of ZEN and the more extensive pre-systemic biotransformation of

293

ZEN to α-ZEL in comparison to the two other poultry species.

15 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 16 of 32

294

Supporting Information Available

295

Chemical structure and phase I biotransformation pathways of zearalenone (adapted from

296

Mukherjee21). This material is available free of charge via the Internet at http://pubs.acs.org.

297

References

298

1.

299

mycotoxin screening reveals the occurrence of 139 different secondary metabolites in feed

300

and feed ingredients. Toxins (Basel) 2013, 5, 504-23.

301

2.

302

and deoxynivalenol on different non-reproductive and reproductive organs in female pigs: A

303

review. Food Addit Contam 2007, 24, 306-314.

304

3.

305

mycotoxins with estradiol binding sites in the mouse uterus. J Toxicol Environ Health 1979, 5,

306

593-8.

307

4.

308

P. T.; van der Burg, P.; Gustafsson, J. A., Interaction of estrogenic chemicals and

309

phytoestrogens with estrogen receptor beta. Endocrinology 1998, 139, 4252-4263.

310

5.

311

hepatic biotransformation of zearalenone. Vet J 2006, 172, 96-102.

312

6.

313

deoxynivalenol (DON) in the pig. Archives of Animal Nutrition-Archiv Fur Tierernahrung 2004,

314

58, 169-180.

315

7.

316

Lindner, W., Concentration levels of zearalenone and its metabolites in urine, muscle tissue,

Streit, E.; Schwab, C.; Sulyok, M.; Naehrer, K.; Krska, R.; Schatzmayr, G., Multi-

Tiemann, U.; Danicke, S., In vivo and in vitro effects of the mycotoxins zearalenone

Greenman, D. L.; Mehta, R. G.; Wittliff, J. L., Nuclear interaction of Fusarium

Kuiper, G. G. J. M.; Lemmen, J. G.; Carlsson, B.; Corton, J. C.; Safe, S. H.; van der Saag,

Malekinejad, H.; Maas-Bakker, R.; Fink-Gremmels, J., Species differences in the

Dänicke, S.; Valenta, H.; Doll, S., On the toxicokinetics and the metabolism of

Zollner, P.; Jodlbauer, J.; Kleinova, M.; Kahlbacher, H.; Kuhn, T.; Hochsteiner, W.;

16 ACS Paragon Plus Environment

Page 17 of 32

Journal of Agricultural and Food Chemistry

317

and liver samples of pigs fed with mycotoxin-contaminated oats. J Agr Food Chem 2002, 50,

318

2494-2501.

319

8.

320

metabolism, detoxification, regulations and intake of zearalenone: an oestrogenic

321

mycotoxin. Food Chem Toxicol 2007, 45, 1-18.

322

9.

323

Biotransformation of zeranol: disposition and metabolism in the female rat, rabbit, dog,

324

monkey and man. Xenobiotica 1983, 13, 209-21.

325

10.

326

Backer, P.; Croubels, S., Toxicokinetic study and absolute oral bioavailability of

327

deoxynivalenol, T-2 toxin and zearalenone in broiler chickens. Food Chem Toxicol 2013, 51,

328

350-5.

329

11.

330

Hens. J Agr Food Chem 1980, 28, 286-291.

331

12.

332

Chickens. Poultry Sci 1980, 59, 1577-1577.

333

13.

334

of Dietary Zearalenone on Reproduction of Chickens. Poultry Sci 1981, 60, 1165-1174.

335

14.

336

2-Toxin, and Zearalenone on Reproduction of Turkey Females. Poultry Sci 1983, 62, 282-289.

337

15.

338

Concentrations of Dietary Zearalenone by Young Male Turkey Poults. Poultry Sci 1986, 65,

339

1905-1910.

Zinedine, A.; Soriano, J. M.; Molto, J. C.; Manes, J., Review on the toxicity, occurrence,

Migdalof, B. H.; Dugger, H. A.; Heider, J. G.; Coombs, R. A.; Terry, M. K.,

Osselaere, A.; Devreese, M.; Goossens, J.; Vandenbroucke, V.; De Baere, S.; De

Dailey, R. E.; Reese, R. E.; Brouwer, E. A., Metabolism of [Zearalenone-C-14 in Laying

Allen, N. K.; Aakhusallen, S.; Mirocha, C. J., Effect of Zearalenone on Reproduction of

Allen, N. K.; Mirocha, C. J.; Aakhusallen, S.; Bitgood, J. J.; Weaver, G.; Bates, F., Effect

Allen, N. K.; Peguri, A.; Mirocha, C. J.; Newman, J. A., Effects of Fusarium Cultures, T-

Olsen, M.; Mirocha, C. J.; Abbas, H. K.; Johansson, B., Metabolism of High-

17 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 18 of 32

340

16.

De Baere, S.; Goossens, J.; Osselaere, A.; Devreese, M.; Vandenbroucke, V.; De

341

Backer, P.; Croubels, S., Quantitative determination of T-2 toxin, HT-2 toxin, deoxynivalenol

342

and deepoxy-deoxynivalenol in animal body fluids using LC-MS/MS detection. Journal of

343

Chromatography B 2011, 879, 2403-2415.

344

17.

345

Volume 8: Notice to applicants and guideline on the establishment of maximum residue limits

346

(MRLs) for residues of veterinary medicinal products in foodstuffs of animal origin. 2005 weblink:

347

http://ec.europa.eu/health/files/eudralex/vol-8/pdf/vol8_10-2005_en.pdf

348

May 4, 2015).

349

18.

350

Kinetics of Veterinary Drugs in Food-Producing Animals: Validation of Analytical Methods Used in

351

Residue Depletion Studies. 2015 weblink:

352

http://www.fda.gov/downloads/AnimalVeterinary/GuidanceComplianceEnforcement/GuidanceforIn

353

dustry/UCM207942.pdf (consulted on May 4, 2015).

354

19.

355

Quantitative determination of zearalenone and its major metabolites in animal plasma using

356

LC-MS/MS and (U)HPLC-HR-MS detection. Analytica Chimica Acta 2012, 756, 37-48.

357

20.

358

Miles, C. O., Preparative enzymatic synthesis of glucuronides of zearalenone and five of its

359

metabolites. J Agr Food Chem 2008, 56, 4032-4038.

360

21.

361

V.; Zarbl, H.; Georgopoulos, P. G., Physiologically-Based Toxicokinetic Modeling of

362

Zearalenone and Its Metabolites: Application to the Jersey Girl Study. Plos One 2014, 9.

European Union. The rules governing medicinal products in the European Union

(consulted

on

VICH GL49(R). Guidance for Industry Studies to Evaluate the Metabolism and Residue

De Baere, S.; Osselaere, A.; Devreese, M.; Van Haecke, L.; De Backer, P.; Croubels, S.,

Stevenson, D. E.; Hansen, R. P.; Loader, J. I.; Jensen, D. J.; Cooney, J. M.; Wilkins, A. L.;

Mukherjee, D.; Royce, S. G.; Alexander, J. A.; Buckley, B.; Isukapalli, S. S.; Bandera, E.

18 ACS Paragon Plus Environment

Page 19 of 32

Journal of Agricultural and Food Chemistry

363

22.

Pfeiffer, E.; Hildebrand, A.; Mikula, H.; Metzler, M., Glucuronidation of zearalenone,

364

zeranol and four metabolites in vitro: Formation of glucuronides by various microsomes and

365

human UDP-glucuronosyltransferase isoforms. Mol Nutr Food Res 2010, 54, 1468-1476.

366

23.

367

De Backer, P.; Croubels, S., Toxicokinetic study and oral bioavailability of deoxynivalenol in

368

turkey poults, and comparative biotransformation between broilers and turkeys World

369

Mycotoxin J 2015, in press.

370

24.

371

the relative roles of cytochromes P450 1A5 and 3A37. Toxicol Appl Pharmacol 2011, 254,

372

349-54.

373

25.

374

Springer Publishers, New York, USA.

Devreese, M.; Antonissen, G.; Broekaert, N.; De Mil, T.; De Baere, S.; Vanhaecke, L.;

Rawal, S.; Coulombe, R. A., Jr., Metabolism of aflatoxin B1 in turkey liver microsomes:

Chen, C-H. Activation and Detoxification Enzymes: Functions and Implications. 2012,

19 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 20 of 32

375

Figure Captions

376

Figure 1. Plasma concentration-time profile of zearalenone (ZEN), α-zearalenol (α-ZEL) and

377

β-zearalenol (β-ZEL) after intravenous (IV) and oral (PO) administration of 3 mg ZEN/kg body

378

weight to broiler chickens (A), laying hens (B) and turkey poults (C) (n=6). Values are

379

presented as mean + SD.

380

Figure 2. Ratio of the peak area detected by ultra-high performance liquid chromatography

381

coupled to high resolution-mass spectrometry of zearalenone (ZEN) or its metabolites,

382

namely α-zearalenol (α-ZEL), β-zearalenol (β-ZEL), ZEN-glucuronide (ZEN-GlcA) and ZEL-

383

glucuronide (ZEL-GlcA), and the internal standard (13C18-ZEN) plotted against the time after

384

intravenous (IV) or oral (PO) administration (p.a.) of 3 mg ZEN/kg body weight to broiler

385

chickens (A), laying hens (B) or turkey poults (C) (n=6). Values are presented as mean + SD.

20 ACS Paragon Plus Environment

Page 21 of 32

Journal of Agricultural and Food Chemistry

21 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 22 of 32

Table 1. Main Toxicokinetic Parameters Of Zearalenone After Oral (PO) And Intravenous (IV) Administration (3 mg/kg BW) To Broiler Chickens, Laying Hens And Turkey Poults (n=6). Values Are Presented As Mean ± SD. Broiler chickens Laying hens Turkey poults PO

IV

PO

IV

PO

IV

39.17 ± 18.67 a,b

2607.0 ± 506.03 a

54.12 ± 22.90 a

2789.2 ± 189.78 a

8.33 ± 2.21 b

700.5 ± 301.18 b

Tmax (h) e

0.35 ± 0.16 a

/

0.32 ± 0.08 a

/

0.97 ± 0.36 b

/

AUC0-t (h.ng/mL) f

21.87 ± 12.12 a,b

290.9 ± 72.78 a

29.31 ± 6.78 a

322.8 ± 37.27 a

8.53 ± 3.07 b

180.0 ± 21.12 b

AUC0-inf (h.ng/mL) g

23.59 ± 15.62 a

292.1 ± 72.50 a

30.04 ± 6.45 a

324.9 ± 35.94 a

10.21 ± 5.57 b

183.1 ± 18.92 b

ka (h-1) h

3.36 ± 1.52 a

/

3.50 ± 1.41 a

/

3.68 ± 2.28 a

/

T1/2a (h) i

0.26 ± 0.10 a

/

0.24 ± 0.09 a

/

0.30 ± 0.19 a

/

MRT (h) j

0.53 ± 0.13 a

0.16 ± 0.02 a

0.53 ± 0.07 a

0.22 ± 0.04 a,b

0.68 ± 0.19 a

0.33 ± 0.09 b

MAT (h) k

0.37 ± 0.14 a

/

0.35 ± 0.13 a

/

0.44 ± 0.27 a

/

Cl (L/h/kg) l

9.06 ± 4.61 a

11.1 ± 2.91 a

11.38 ± 3.03 a

9.39 ± 1.08 a

19.66 ± 3.87 b

16.57 ± 1.64 b

kel (h-1) m

2.14 ± 0.35 a

2.86 ± 1.06 a

1.98 ± 0.37 a

1.72 ± 0.07 a

2.04 ± 0.57 a

1.83 ± 0.10 a

T1/2el (h) n

0.34 ± 0.07 a

0.29 ± 0.11 a

0.36 ± 0.07 a

0.46 ± 0.12 a

0.35 ± 0.10 a

0.38 ± 0.02 a

Cmax (PO) c or C0 (IV) d (ng/mL)

22

ACS Paragon Plus Environment

Page 23 of 32

Journal of Agricultural and Food Chemistry

Vd (L/kg) o

3.21 ± 2.13 a

4.16 ± 0.75 a

6.18 ± 2.52 a

6.24 ± 0.92 a

10.65 ± 1.05 b

9.03 ± 1.43 b

F (%) p

8.34 ± 5.96 a

100 a

10.28 ± 2.53 a

100 a

6.87 ± 3.54 a

100 a

A different superscript (a or b) denotes a significant difference between animal species for each administration route at p < 0.05 Cmax: maximal plasma concentration, d C0: plasma concentration at time 0, e Tmax: time to maximal plasma concentration, f AUC0-t: area under the plasma concentration-time curve from time 0 to 3 h; g AUC0-inf: area under the plasma concentration-time curve from time 0 to infinite, h ka: absorption rate constant, i T1/2a: absorption half-life, j MRT: mean residence time, k MAT: mean absorption time, l Cl: total body clearance, m kel: elimination rate constant, n T1/2el: elimination half-life, o Vd: volume of distribution, p F: absolute oral bioavailability c

23

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 24 of 32

Table 2. Main Toxicokinetic Parameters Of α- And β-zearalenol (α-/β-ZEL) After Oral (PO) And Intravenous (IV) Administration Of Zearalenone (3 mg/kg BW) To Broiler Chickens, Laying Hens And Turkey Poults (n=6). Values Are Presented As Mean ± SD. Broiler chickens Laying hens Turkey poults PO

IV

PO

IV

PO

IV

Cmax (ng/mL) c

3.99 ± 2.53 a

30.31 ± 10.23 a

3.20 ± 1.99 a

37.91 ± 10.07 a

6.45 ± 0.33 a

27.32 ± 2.21 a

Tmax (h) d

0.63 ± 0.11 a

0.03 ± 0.00 a

0.27 ± 0.08 a

0.03 ± 0.00 a

0.58 ± 0.08 a

0.09 ± 0.03 b

AUC0-t (h.ng/mL) e

2.44 ± 0.80 a

5.68 ± 1.61 a

1.57 ± 0.87 a

6.81 ± 1.80 a

11.60 ± 0.14 b

17.71 ± 2.35 b

AUC0-inf (h.ng/mL) f

2.79 ± 1.37 a

5.93 ± 1.68 a

1.63 ± 0.89 a

6.99 ± 1.75 a

15.58 ± 8.39 b

20.04 ± 5.12 b

Cmax (ng/mL) c

25.25 ± 13.96 a

13.30 ± 6.48 a

96.16 ± 38.95 b

38.92 ± 16.14 b

28.52 ± 15.36 a

15.14 ± 1.61 a

Tmax (h) d

0.61 ± 0.11 a

0.07 ± 0.19 a

0.42 ± 0.08 a,b

0.03 ± 0.00 a

0.37 ± 0.14 b

0.15 ± 0.03 b

AUC0-t (h.ng/mL) e

24.55 ± 15.09 a

3.50 ± 1.51 a

58.48 ± 14.60 a

6.64 ± 2.81 b

29.66 ± 13.43 a

9.83 ± 1.43 b

AUC0-inf (h.ng/mL) f

27.36 ± 17.51 a

4.09 ± 1.87 a

58.84 ± 14.54 a

6.90 ± 2.71 a

38.83 ± 20.04 a

15.36 ± 3.42 b

α-ZEL/ZEN g

0.138 ± 0.073 a

0.020 ± 0.001 a

0.057 ± 0.026 a

0.021 ± 0.004 a

1.015 ± 0.369 b

0.109 ± 0.033 b

β-ZEL/ZEN h

1.607 ± 1.159 a

0.018 ± 0.011 a

2.029 ± 0.262 a

0.021 ± 0.006 a

4.888 ± 3.124 a

0.089 ± 0.028 b

α-ZEL

β-ZEL

24

ACS Paragon Plus Environment

Page 25 of 32

Journal of Agricultural and Food Chemistry

ZEL/ZEN i

1.149 ± 0.525 a

0.032 ± 0.009 a

2.086 ± 0.271 a

0.042 ± 0.009 a

5.226 ± 2.898 b

0.152 ± 0.040 b

α-ZEL/β-ZEL j

0.153 ± 0.049 a

1.629 ± 0.566 a

0.027 ± 0.013 a

1.073 ± 0.151 a

0.749 ± 0.292 b

1.076 ± 0.243 a

A different superscript (a or b) denotes a significant difference between animal species for each administration route at p < 0.05 c Cmax: maximal plasma concentration, d Tmax: time to maximal plasma concentration, e AUC0-t: area under the plasma concentration-time curve from time 0 to 2 or 3 h, f AUC0-inf: area under the plasma concentration-time curve from time 0 to infinite, g α-ZEL/ZEN = (AUC0-inf α-ZEL) / (AUC0-inf ZEN), h β-ZEL/ZEN = (AUC0-inf β-ZEL) / (AUC0-inf ZEN), i ZEL/ZEN = (AUC0-inf α-ZEL + AUC0-inf β-ZEL) / (AUC0-inf ZEN), j α-ZEL/β-ZEL = (AUC0-inf α-ZEL ) / (AUC0-inf β-ZEL)

25

ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 26 of 32

Figure 1 (A)

Plasma concentration (ng/mL)

IV 10000.0 1000.0 100.0 ZEN 10.0

α-ZEL β-ZEL

1.0 0.1 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

Plasma concentration (ng/mL)

PO 100.00

10.00

1.00

ZEN α-ZEL

0.10

β-ZEL

0.01 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

26 ACS Paragon Plus Environment

Page 27 of 32

Journal of Agricultural and Food Chemistry

(B)

Plasma concentration (ng/mL)

IV 10000.0 1000.0 100.0 ZEN 10.0

α-ZEL β-ZEL

1.0 0.1 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

Plasma concentration (ng/mL)

PO 1000.00 100.00 10.00 ZEN 1.00

α-ZEL β-ZEL

0.10 0.01 0.0

0.5

1.0

1.5

2.0

Time p.a. (h)

27 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 28 of 32

(C)

Plasma concentration (ng/mL)

IV 1000

100 ZEN α-ZEL

10

β-ZEL 1 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

Plasma concentration (ng/mL)

PO 100.00

10.00

1.00

ZEN α-ZEL

0.10

β-ZEL

0.01 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

28 ACS Paragon Plus Environment

Page 29 of 32

Journal of Agricultural and Food Chemistry

Figure 2 (A)

IV 1000.000

Area ratios

100.000 10.000

ZEN

1.000

α-ZEL

0.100

β-ZEL ZEN-GlcA

0.010

ZEL-GlcA 0.001 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

PO 10.000

Area ratios

1.000 ZEN 0.100

α-ZEL β-ZEL

0.010

ZEN-GlcA ZEL-GlcA

0.001 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

29 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 30 of 32

(B)

IV 1000.000

Area ratios

100.000 10.000

ZEN

1.000

α-ZEL

0.100

β-ZEL ZEN-GlcA

0.010

ZEL-GlcA 0.001 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

PO 10.000

Area ratios

1.000 ZEN 0.100

α-ZEL β-ZEL

0.010

ZEN-GlcA ZEL-GlcA

0.001 0.0

0.5

1.0

1.5

2.0

Time p.a. (h)

30 ACS Paragon Plus Environment

Page 31 of 32

Journal of Agricultural and Food Chemistry

(C)

IV Area ratios

100.00 10.00 ZEN

1.00

α-ZEL β-ZEL

0.10

ZEN-GlcA 0.01 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

PO Area ratios

10.000 1.000 ZEN

0.100

α-ZEL β-ZEL

0.010

ZEL-GlcA 0.001 0.0

0.5

1.0

1.5

2.0

2.5

3.0

Time p.a. (h)

31 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 32 of 32

Graphic for Table Of Contents (TOC)

32 ACS Paragon Plus Environment