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Application No.: VFD0188 Version 1  12/2020

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No blood(y) stress –Phenolic antioxidants in olive oil and olive oil wastewater

Juliane Böttcher, Kate Monks; applications@knauer.net

KNAUER Wissenschaftliche Geräte GmbH, Hegauer Weg 38, 14163 Berlin

No blood(y) stress –Phenolic antioxidants in olive oil and olive oil wastewater

Foto: pexels-pixabay

Summary

The content of polyphenols, or biophenols, in olive oil is interesting due to their attributed benefits and impact on human health. Only with a certain amount of biophenols the manufacturer can advertise the product to have a positive effect on health [1]. But also, the wastewater incurring in olive oil production can still contain the coveted polyphenols. These wastewaters, which are mostly discarded, might be a source for a possible recovery of these biologically interesting constituents [2].

Introduction

Polyphenols are secondary plant compounds that can offer various health benefits. They can act as antioxidants or be helpful due to their anti-inflammatory effects, for example. There are many foods, plants and vegetables which are rich in polyphenols but in this application the focus was set on olive oil and wastewater from olive oil production. With Commission Regulation (EU) No 432/2012 of 16 May 2012 a list of permitted health claims made on food was established3. Referring to this list, olive oils can be labeled with the addition “Olive oil polyphenols contribute to the protection of blood lipids from oxidative stress”. The claim may be used only for olive oil which contains at least 5 mg of hydroxytyrosol and its derivatives (e.g. oleuropein complex and tyrosol) per 20 g of olive oil. In order to bear the claim information shall be given to the consumer that the beneficial effect is obtained with a daily intake of 20 g of olive oil [3]. The profile of biophenolic compounds in olive oils and its wastewater is quite complex with far over 20 possible substances. A detailed method for profiling olive oil samples is provided by the International Olive Council4. Most of the used standards described in that method are commercially unavailable, thus in the following application the determination of only eight compounds (3-hydroxytyrosol, tyrosol, 4-hydroxyphenylacetic acid, vanillic acid, caffeic acid, syringic acid, oleuropein, and quercetin) was conducted with an adapted method.

Results

For peak identification, single standards of the eight phenolic compounds were measured. Thereafter a mixed standard stock solution was prepared. For calibration, the stock solution was diluted to five different levels (Tab. 1).

Chromatogram of mixed standard at calibration level 5. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - 4-hydroxyphenylacetic acid, 4 - Vanillic acid, 5 - Caffeic acid, 6 - Syringic acid, 7 - Oleuropein, 8 - Quercetin.

Fig. 1 Chromatogram of mixed standard at calibration level 5.
1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - 4-hydroxyphenylacetic acid, 4 - Vanillic acid, 5 - Caffeic acid, 6 - Syringic acid, 7 - Oleuropein, 8 - Quercetin.

Tab. 1 Concentrations of calibration levels

Substance

Level 1
(µg/ml)

Level 2 (µg/ml)

Level 3 (µg/ml)

Level 4 (µg/ml)

Level 5 (µg/ml)

3-Hydroxyty-rosol

4.400

6.600

13.200

66.000

132.000

Tyrosol

1.233

1.850

3.700

18.500

37.000

4-Hydroxyphenylacetic acid

1.967

2.950

5.900

29.500

59.000

Vanillic acid

0.867

1.300

2.600

13.000

26.000

Caffeic acid

1.367

2.050

4.100

20.500

41.000

Syringic acid

0.867

1.300

2.600

13.000

26.000

Oleuropein

1.967

2.950

5.900

29.500

59.000

Quercetin

0.733

1.100

2.200

11.000

22.000

The calibration was successful with a linearity of R2 ≥ 0.9996 for all compounds. Based on the calibration measurements the limit of detection (LOD) and limit of quantification (LOQ) were calculated (Tab. 2). For LOD a signal-to-noise ratio (S/N) of S/N=3 was taken as basis of calculation and for LOQ a ratio of S/N=10 was specified.

Tab. 2 Calculated LOD and LOQ

Substance

LOD S/N=3 (µg/ml)

LOQ S/N=10 (µg/ml)

3-Hydroxytyrosol

0.794

2.645

Tyrosol

1.316

4.386

4-Hydroxyphenylacetic acid

1.944

6.481

Vanillic acid

0.641

2.138

Caffeic acid

0.382

1.274

Syringic acid

0.463

1.543

Oleuropein

1.963

6.542

Quercetin

0.431

1.437

Five commercially available olive oils were tested and prepared according to the Internal Olive Council sample preparation method (section 5.1) [4] with the changes mentioned in the sample preparation section. All samples were marked as “native extra” but none of the samples was labelled according to Health Claims Regulation. Exemplarily two chromatograms of olive oil samples are shown. Three of the calibrated substances were detected in the sample (Fig. 2). Except for 3-hydroxytyrosol the calculated amounts were below the LOQ of the method.

Chromatogram of olive oil sample 2. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - vanillic acid.

Fig. 2 Chromatogram of olive oil sample 2. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - vanillic acid.

Results

Amounts of phenols in samples in mg/20g.

Fig. 3 Amounts of phenols in samples in mg/20g.

In the second sample also some of the calibrated compounds were detected. Again except for 3-hydroxytyrosol the amounts were below the calculated limit of quantification or even limit of detection. The detectable substances were quantified (Tab. 3, Fig. 5). Caffeic acid and 4-hydroxyphenylacetic acid were neither found in olive oil nor in wastewater samples.

Tab. 3 Results of sample measurement, *= below LOQ/LOD

Substance

Sample 1 (µg/ml)

Sample 2 (µg/ml)

Sample 3 (µg/ml)

Sample 4 (µg/ml)

Sample 5 (µg/ml)

3-Hydroxyty-

rosol

4.107

3.641

6.375

3.433

4.289

Tyrosol

2.620*

2.594*

4.107*

2.813*

3.352*

Vanillic acid

-

0.393*

-

-

-

Syringic acid

0.322*

-

0.386*

-

0.207*

Oleuropein

1.375*

-

-

-

1.859*

Quercetin

1.131*

-

-

1.430*

1.623

Chromatogram of olive oil sample 3. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - Syringic acid.

Fig. 4 Chromatogram of olive oil sample 3. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - Syringic acid.

Tyrosol and 3-hydroxytyrosol were found in each of the five samples whereas the other calibrated compounds show different composition patterns. Instead of using an internal standard, the recovery rate was determined. Therefore, one of the samples was spiked with the mixed standard at different concentrations and extracted according to sample preparation procedure.

Tab. 4 Recovery rate for extraction procedure

Substance

Recovery rate (%)

3-Hydroxytyrosol

99.77

Tyrosol

92.28

4-Hydroxyphenylacetic acid

88.86

Vanillic acid

98.96

Caffeic acid

92.20

Syringic acid

90.25

Oleuropein

52.93

Quercetin

73.77

Furthermore, two wastewater samples from an olive oil production process were measured. The target was to verify if the wastewater still contains amounts of polyphenols which could be of interest for recovery and/or re-use. Recovery rates for the wastewater samples were not determined.

Chromatogram of olive oil wastewater sample 1. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - Vanillic acid.

Fig. 5 Chromatogram of olive oil wastewater sample 1. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - Vanillic acid.

Chromatogram of olive oil wastewater sample 2. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - Oleuropein.

Fig. 6 Chromatogram of olive oil wastewater sample 2. 1 - 3-hydroxytyrosol, 2 - Tyrosol, 3 - Oleuropein.

Both wastewater samples contain high residues of 3-hydroxytyrosol and tyrosol as well as small amounts of other of the calibrated substances (Tab. 5).

Tab. 5 Recovery rate for extraction procedure

Substance

Wastewater 1 (µg/ml)

Wastewater 2 (µg/ml)

3-Hydroxytyrosol

537.336

179.115

Tyrosol

484.373

413.389

4-Hydroxyphenylacetic acid

-

-

Vanillic acid

16.258

-

Caffeic acid

-

-

Syringic acid

-

-

Oleuropein

-

48.740

Quercetin

-

-

The application was realized with the kind support of the FiW - Research Institute for Water and Waste Management at RWTH Aachen e. V. and the Institute for Applied Polymer Chemistry (IAP) of FH Aachen. The work was carried out within the CLIENT II research project „I-WALAMAR“ (FKZ: 01LZ1807C).

Sample Preparations

Single standards were dissolved in methanol. Out of these single standards a mixed standard was prepared. Olive oil samples were prepared according to International Olive Council method (section 5.1 Sample preparation) [4], but without the use of an internal standard. Furthermore, the 0.45 µm PVDF (polyvinylidene fluoride) filter was replaced by a 0.45 µm RC (regenerated cellulose) filter. Wastewater samples were prepared with manual solid phase extraction using CHROMABOND C18, 45 µm, 3 ml/500 mg SPE columns5. The applied SPE method was taken from the Macherey Nagel application database [6].

SPE method parameters

Fig. 7 SPE method parameters

Conclusion

Although the measured olive oil samples were not labelled with the claim “Olive oil polyphenols contribute to the protection of blood lipids from oxidative stress” [3], the samples would meet the requirements. For all extracts an amount of at least 5 mg of 3-hydroxytyrosol and its derivatives (e.g. oleuropein complex and tyrosol) per 20 g of olive oil were determined (Tab. 3, Fig. 4). The analyzed wastewater samples showed high amounts of 3-hydroxytyrosol and tyrosol (Tab. 5). With an appropriate sample preparation and possibly preparative HPLC purification, it should be feasible to recover these substances and make them usable for other areas of application.

References

[1] Olea. https://www.oelea.de/olivenoel-analyse-polyphenole (2020/05/11).

[2] Mulinacci, N. et al. Polyphenolic content in olive oil waste waters and related olive samples. Journal of Agricultural and Food Chemistry 49(8):3509-14 (2001).

[3] Official journal of the european union. Commission regulation (EU) No 432/2012. https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:32012R0432&from=EN (2020/06/11).

[4] International olive council. Determination of biophenols in olive oils by HPLC. https://www.internationaloliveoil.org/wp-content/uploads/2019/11/COI-T.20-Doc.-No-29-Rev-1-2017.pdf (2020/06/11).

[5] Macherey-Nagel. Solid phase extraction. https://www.mn-net.com/de/spe-columns-chromabond-c18-45-m-3-ml/500-mg-730003?c=4514 (2020/06/11).

[6] Macherey-Nagel. Determination of twenty phenolic compounds from Alperujo (A semisolid waste from the olive oil industry). https://chromaappdb.mn-net.com/SPE/9D0DD88B-3C0E-27CA-7712-C260CB3F95EC/determination-of-twenty-phenolic-compounds-from-alperujo-a-semisolid-waste-from-the-olive-oil-industry (2020/06/11).

Materials and Methods

Tab. 6 Method settings

Column temperature

30 °C

Injection volume

10 µl

Injection mode

Partial loop

Detection

UV 280 nm

Data rate

20 Hz

Time constant

0.05 s

Tab. 7 Pump parameters

Eluent (A)

0.2% phosphoric acid



Eluent (B)

methanol



Flow rate

1.2 ml/min



Gradient

Time (min)

% A

% B


0

90

10


3

80

20


10

75

25


18

0

100


20

0

100


20.02

90

10


23

90

10

Tab. 8 System configuration

Instrument

Description

Article No.

Pump 1

AZURA P6.1L HPG, 10 ml

APH35EA

Autosampler

AZURA AS 6.1L

AAA00AA

Detector

AZURA DAD 6.1L

ADC11

Flow cell

Analytical KNAUER pressureproof UV flow cell cartridge

AMC38

Thermostat

AZURA CT 2.1

ATC00

Column

Eurospher II 100-5 C18A, 250 x 4 mm ID with precolumn

25WE184E2J

Software

ClarityChrom 8.2.3 – Workstation, autosampler control included

A1670

Software

ClarityChrom 8.2.3 – PDA extension

A1676

KNAUER HPLC System Configuration

Application details

Method

HPLC

Mode

RP

Substances

3-Hydroxytyrosol, Tyrosol, 4-Hydroxyphenylacetic acid, Vanillic acid, Caffeic acid, Syringic acid, Oleuropein, Quercetin

CAS number

10597-60-1, 331-39-5, 32619-42-4, 156-38-7, 501-94-0, 117-39-5, 530-57-4, 121-34-6

Version

Application No.: VFD0188 | Version 1  12/2020 | ©KNAUER Wissenschaftliche Geräte GmbH