7
ORIGINAL ARTICLE Utilization of seeds from tomato processing wastes as raw material for oil production Cristina Botines ¸tean Alexandra Teodora Gruia Ionel Jianu Received: 19 April 2013 / Accepted: 9 January 2014 Ó Springer Japan 2014 Abstract The increase of waste quantities from tomato processing industry is an important ecological and also financial problem. Seeds are the major component of this waste and one valuable alternative of transforming them into raw materials is oil extraction. The isolated oil can be used for nutritive or industrial purposes. In this research, the influence of some extraction parameters (time, solvent and granularity of tomato milled seeds) on the fatty acid (FA) composition, water content and water reaction rate has been evaluated. The FA composition of tomato seed oil, determined by gas chromatography–mass spectrome- try, has shown a high content of linoleic acid (20.8–39.9 mg/mL), followed by palmitic acid (6.3–19.3 mg/mL), oleic acid (2.5–14.2 mg/mL), linolenic acid (0.7–4.9 mg/mL), stearic acid (0.1–0.8 mg/mL), pal- mitoleic acid (0.03–0.5 mg/mL), arachidic acid (0.08–0.4 mg/mL), myristic acid (0.05–0.2 mg/mL) and margaric acid (0.02–0.11 mg/mL). The oil content of tomato seeds was registered in the range of 13.3–19.3 %. For evaluation of water content, a method using Karl Fischer titration (KFT) has been established. Comparing with the physical methods that do not distinguish the water content from volatile matter, KFT is an important tech- nique, very accurate, that determines water content by a chemical reaction. Keywords Waste Á Tomato seeds Á Fatty acids Introduction Industrial processing of tomatoes conducts to a very high amount of waste, and seeds are the major by-product. Just a small amount of these seeds are used as feeds or fertilizers, and the rest of quantity represents an environmental pol- lution problem. The processors were thinking on different ways to capitalize tomato seeds resulting from the tomato processing industry, to increase the profit from this industry [13]. One application of using waste from tomato pro- cessing industry is to obtain oil from tomato seeds by extraction. Fewer applications that imply the extraction and ana- lysis of tomato oil extracted from tomato seeds are reported in literature. Regarding the fatty acid (FA) composition of tomato seed oil, the major FA component was linoleic acid (C18:2), with a concentration range of 37–57 %. The main saturated FA identified was palmitic acid (C16:0), with a concentration range from 7 to 24 %. Other important FA identified in tomato seed oil were: oleic acid (C18:1) 18–30 %, stearic acid (C18:0) 4–13 %, and linolenic acid (C18:3) 1–6 %. Small amounts of myristic acid (C14:0) 0.1–2.3 %, palmitoleic acid (C16:1) (0.3–7 %), margaric acid (C17:0) 0.1–0.3 % and arachidic acid (C20:0) (0.2–3 %) have been reported [411]. Behenic, lignoceric, Authors declare that a small part of this paper has been presented as an oral presentation entitled: ‘‘Water determination for tomato seed oil extracts using Karl Fischer titration’’ at the scientific meeting: 3rd International Conference on Food Chemistry, Engineering and Technology (2012), Timisoara, Romania. C. Botines ¸tean (&) Á I. Jianu Food Technology Department, Banat’s University of Agricultural Sciences and Veterinary Medicine of Timis ¸oara, Calea Aradului 119, 300645 Timisoara, Romania e-mail: [email protected] A. T. Gruia Regional Center for Transplant Immunology, Emergency Timis ¸ County Hospital, Bv. Iosif Bulbuca 10, 300736 Timisoara, Romania 123 J Mater Cycles Waste Manag DOI 10.1007/s10163-014-0231-4

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Page 1: Utilization of seeds from tomato processing wastes as raw material for oil production

ORIGINAL ARTICLE

Utilization of seeds from tomato processing wastes as raw materialfor oil production

Cristina Botinestean • Alexandra Teodora Gruia •

Ionel Jianu

Received: 19 April 2013 / Accepted: 9 January 2014

� Springer Japan 2014

Abstract The increase of waste quantities from tomato

processing industry is an important ecological and also

financial problem. Seeds are the major component of this

waste and one valuable alternative of transforming them

into raw materials is oil extraction. The isolated oil can be

used for nutritive or industrial purposes. In this research,

the influence of some extraction parameters (time, solvent

and granularity of tomato milled seeds) on the fatty acid

(FA) composition, water content and water reaction rate

has been evaluated. The FA composition of tomato seed

oil, determined by gas chromatography–mass spectrome-

try, has shown a high content of linoleic acid

(20.8–39.9 mg/mL), followed by palmitic acid

(6.3–19.3 mg/mL), oleic acid (2.5–14.2 mg/mL), linolenic

acid (0.7–4.9 mg/mL), stearic acid (0.1–0.8 mg/mL), pal-

mitoleic acid (0.03–0.5 mg/mL), arachidic acid

(0.08–0.4 mg/mL), myristic acid (0.05–0.2 mg/mL) and

margaric acid (0.02–0.11 mg/mL). The oil content of

tomato seeds was registered in the range of 13.3–19.3 %.

For evaluation of water content, a method using Karl

Fischer titration (KFT) has been established. Comparing

with the physical methods that do not distinguish the water

content from volatile matter, KFT is an important tech-

nique, very accurate, that determines water content by a

chemical reaction.

Keywords Waste � Tomato seeds � Fatty acids

Introduction

Industrial processing of tomatoes conducts to a very high

amount of waste, and seeds are the major by-product. Just a

small amount of these seeds are used as feeds or fertilizers,

and the rest of quantity represents an environmental pol-

lution problem. The processors were thinking on different

ways to capitalize tomato seeds resulting from the tomato

processing industry, to increase the profit from this industry

[1–3]. One application of using waste from tomato pro-

cessing industry is to obtain oil from tomato seeds by

extraction.

Fewer applications that imply the extraction and ana-

lysis of tomato oil extracted from tomato seeds are reported

in literature.

Regarding the fatty acid (FA) composition of tomato

seed oil, the major FA component was linoleic acid

(C18:2), with a concentration range of 37–57 %. The main

saturated FA identified was palmitic acid (C16:0), with a

concentration range from 7 to 24 %. Other important FA

identified in tomato seed oil were: oleic acid (C18:1)

18–30 %, stearic acid (C18:0) 4–13 %, and linolenic acid

(C18:3) 1–6 %. Small amounts of myristic acid (C14:0)

0.1–2.3 %, palmitoleic acid (C16:1) (0.3–7 %), margaric

acid (C17:0) 0.1–0.3 % and arachidic acid (C20:0)

(0.2–3 %) have been reported [4–11]. Behenic, lignoceric,

Authors declare that a small part of this paper has been presented as

an oral presentation entitled: ‘‘Water determination for tomato seed

oil extracts using Karl Fischer titration’’ at the scientific meeting: 3rd

International Conference on Food Chemistry, Engineering and

Technology (2012), Timisoara, Romania.

C. Botinestean (&) � I. Jianu

Food Technology Department, Banat’s University

of Agricultural Sciences and Veterinary Medicine of Timisoara,

Calea Aradului 119, 300645 Timisoara, Romania

e-mail: [email protected]

A. T. Gruia

Regional Center for Transplant Immunology,

Emergency Timis County Hospital, Bv. Iosif Bulbuca 10,

300736 Timisoara, Romania

123

J Mater Cycles Waste Manag

DOI 10.1007/s10163-014-0231-4

Page 2: Utilization of seeds from tomato processing wastes as raw material for oil production

and gondoic acids were also identified in very small

amounts in tomato seed oils [4, 5].

Various methods were used to determine the water

content of foodstuff. Even if thermal methods are prone to

error, they are frequently used because they are inexpen-

sive methods. Analytical methods are based on estimating

moisture by evaporation (‘‘loss of drying’’ or ‘‘oven-dry-

ing’’) and they have been compared with other more effi-

cient methods, one of them being Karl Fischer titration

(KFT) [12]. The disadvantage of thermal methods being

time-consuming can be reduced using Karl Fischer water

determination method [13].

Comparing with the physical methods that not distin-

guish the water content from volatile matter, KFT is an

important technique, very accurate, that determines the

water content by a chemical reaction of the amount of

water that is present in the sample (even in those containing

very low content of water such as oils). KFT technique

allows working with numerous samples in a short time and

automation; these improve reproducibility, repeatability

and accuracy of the experiments [14].

The aim of this study was to evaluate the influence of

some extraction parameters of tomato seed oil on the FA

composition, water content and water reaction rate from

KFT.

Materials and method

Materials

Tomato seeds were collected from tomatoes (Solanum

lycopersicum) cultivated in Timis County, Romania. The

seeds were separated and cleaned from the mixture of peel,

pulp, and seeds, with water, after that they were spread to

dry for 3 days and then kept at 10 �C until extraction. To

obtain different granularity of tomato seed powder that will

serve as raw material for oil extraction, two different lab-

oratory mills were used: electrical mill was used to obtain

tomato seed powder with a granularity \0.5 mm and

mechanical mill to obtain a granularity of tomato seed

powder in the range of 0.5–1.5 mm.

Petroleum ether, diethyl ether, ethanol 96 %, n-hexane

(analytical grade, Sigma-Aldrich), methanol�BF3 (reagent

grade, Fluka) and Standard 37 FAME mix (Supelco) were

used.

Methods

Isolation of oil from tomato seeds

Tomato seed oil was obtained using solid–liquid semi-

continuous Soxhlet extraction method. The percolation

(siphoning cycle), characteristic to Soxhlet extraction

method, represents the importance of extraction time on

tomato oil yield. To optimize the extraction process (by

reducing extraction time) the shortest period of time nec-

essary to obtain tomato oil with approximately maximum

yield (after how many siphoning cycles were not registered

significant differences on oil yield), has been determined.

For studying the influence of the surface contact (between

the tomato seed powder and solvent) on FA composition,

water content and water reaction rate, different granulari-

ties of tomato seed powder were used (as described in

‘‘Materials’’). Also, the influence of extraction solvent on

the FA composition, water content and water reaction

rate has been evaluated using petroleum ether and diethyl

ether.

The following codifications were used for the oil sam-

ples extracted from tomato seeds: DEE––tomato seed oil

extracted with diethyl ether using six percolations and a

granularity of the milled tomato seeds\0.5 mm; PE1/PE2/

PE4/PE6––tomato seed oil extracted with petroleum ether

using 1/2/4/6 percolations (significant differences after 6

percolation were not registered between the values of the

oil yield, therefore an increasing of time expressed in

number of percolation was not necessary) and a granularity

of the milled tomato seeds\0.5 mm, MMPE––tomato seed

oil extracted with petroleum ether using six percolations

and mechanically milled tomato seeds (granularity in the

range of 0.5–1.5 mm).

KFT water determination

Classical Karl Fischer water titration was carried out using

a Karl Fischer 701 Titrando apparatus from Metrohm, a

Metrohm 10 dosing and 703 Ti Stand mixing systems

(Metrohm).

KFT was performed using the two-component tech-

nique: component 1 was Titrant 5 apura and component 2

Solvent apura (both from Merck & Co., Inc.), which con-

tains imidazole, sulfur dioxide in methanolic solution. The

titer of the component 1 was determined using water

standard 1 %, standard for volumetric KFT (Merck).

The tomato seed oil sample amount was in the range of

0.6–1.1 g. The following KFT method parameters were

used: I (pol) of 50 lA, end point and dynamics at 250 mV,

maximum rate of 5 mL/min, drift was used as stop crite-

rion, with a stop drift of 20 lL/min. The titer of the iodine

solution, determined with the water standard solution, was

4.5924 mg/mL. The extraction time was 300 s.

Preparing of FA methyl esters (FAMEs)

Tomato seed oil samples were transmethylated using the

methanol�BF3 method (adapted after Hadaruga et al. [15])

J Mater Cycles Waste Manag

123

Page 3: Utilization of seeds from tomato processing wastes as raw material for oil production

to identify and quantify the FAMEs by gas chromatogra-

phy–mass spectrometry (GC–MS) analysis.

About 25 mg of tomato seed oil was accurately weighed

into a screw cap tube, 5 mL methanol�BF3 solution was

added and refluxed for 2 min on a water bath. After cool-

ing, 5 mL of hexane was added, followed by 1 min of

refluxing and then the solution was treated with 15 mL

saturated NaCl solution under vigorous stirring. The mix-

ture was separated and the organic layer was removed,

dried over anhydrous CaCl2, and used for GC–MS analysis.

GC–MS analysis

A volume of 2 lL of derivatized sample was injected in a

HP 6890 Series Gas Chromatograph coupled with a Hew-

lett Packard 5973 Mass Selective Detector. The gas chro-

matograph was equipped with a split–splitless injector and

a Factor FourTM Capillary Column VF-35ms fused silica

column of 35 % phenyl-methylpolysiloxane, 30 m length,

0.25 mm internal diameter, and 0.25 lm film thickness.

GC conditions include a temperature range of 50–250 �C

with a heating rate of 6 �C/min and a solvent delay of

5 min. The inlet temperature was maintained at 250 �C,

helium was used as GC carrier gas at 1.0 mL/min and the

sample was injected in the splitless mode.

The following MS conditions were used: ionization

energy of 70 eV, quadrupole temperature of 280 �C, scan

rate of 1.6 scan/s and mass detection of 50–550 amu. The

mass spectra of the samples were compared with those

from the NIST/EPA/NIH Mass Spectral Library 2.0 to

identify the main compounds. All samples were monitored

on the scan mode.

Results and discussion

Extraction and physical–chemical analysis of tomato

seed oil

The yields obtained for oil extraction from tomato seeds

were in the range of 13.3–19.3 % (reported to dry weight

basis). The highest yield (19.3 %) was obtained using

petroleum ether for extraction.

Significant variations of classical physical–chemical

values were not registered. Thus, the main characteristics

determined for oil, which was isolated by solid–liquid

semi-continuous extraction from electrically milled tomato

seeds using standard methods [16], were: saponification

value (191 mg KOH/g), acid value (2 mg KOH/g), ester

value (189 mg KOH/g), density at 15 �C (0.9245 kg/m3),

refractive index at 25 �C (nD = 1.4733), and kinematic

viscosity at 40 �C (23 mm2/s).

More important was the FA composition of extracted

tomato seed oils, as well as the trace of water, which has a

negative influence on the oil stability.

FA composition of tomato seed oil

The effects of FA as components of triacylglycerols,

especially those essential (linoleic and linoleic) on the

quality of the final tomato seed oil are very important.

Vegetable oils are the main sources for the intake of

essential polyunsaturated FA and have an important role in

human diets. The FA with the highest concentration in

tomato seed oil is linoleic acid, a polyunsaturated x-6 FA

and contributes to increase the quality of the tomato seed

oil due to its chemical–nutritional–biological relevant

properties. Linoleic acid has an important role in a healthy

brain function, reproductive health, bone density, in the

maintenance of normal cholesterol level [17, 18].

The FA relative concentration of tomato seed oil

(Table 1), determined by GC–MS indicates that the most

concentrated is C18:2 (47–73 %), followed by C16:0 and

C18:1 (14–25 %, respectively, 8–21 %). Other important

identified FA: C18:3 (2–6 %) and C18:0 (0.5–1 %). Some

FA were detected in a lower relative concentrations: C14:0

(0.1–0.3 %), C16:1 (0.1–0.8 %), C17:0 (*0.1 %), and

C20:0 (0.3–0.6 %).

A slight variation of the relative concentration of

FA from derivatized samples of tomato seed oil was

noticed due to the influence of the conditions used for

extraction.

Table 1 The relative concentration (%) of the FA from tomato seed oil extracts

Code C14:0 C16:1 C16:0 C17:0 C18:0 C18:1 C18:2 C18:3 C20:0

DEE 0.14 ± 0 0.05 ± 0.01 18.47 ± 0.01 0.12 ± 0.01 0.51 ± 0.01 20.89 ± 0.07 56.81 ± 0.13 2.59 ± 0.01 0.42 ± 0.04

PE1 0.19 ± 0.02 0.84 ± 0.16 14.24 ± 0.10 0.07 ± 0.01 0.46 ± 0.07 8.60 ± 0.22 72.69 ± 0.58 2.62 ± 0.05 0.28 ± 0.05

PE2 0.24 ± 0.01 0.69 ± 0.02 13.92 ± 0.47 0.08 ± 0.01 0.47 ± 0.01 9.40 ± 0.09 71.78 ± 0.87 3.11 ± 0.29 0.31 ± 0.03

PE4 0.21 ± 0.02 0.68 ± 0.03 14.52 ± 1.31 0.08 ± 0.01 0.55 ± 0.12 9.69 ± 0.50 70.80 ± 2.25 3.19 ± 0.39 0.27 ± 0.03

PE6 0.31 ± 0.02 0.68 ± 0.04 24.82 ± 0.99 0.14 ± 0.01 1.07 ± 0.05 18.23 ± 0.56 47.85 ± 1.91 6.34 ± 0.23 0.55 ± 0.01

MMPE 0.12 ± 0.02 0.05 ± 0 18.16 ± 0.29 0.11 ± 0 0.47 ± 0 20.68 ± 0.29 57.8 ± 0.62 2.28 ± 0.04 0.32 ± 0.03

Results are presented as average of duplicates

J Mater Cycles Waste Manag

123

Page 4: Utilization of seeds from tomato processing wastes as raw material for oil production

The type of the solvent used for extraction does not

influence just the oil yield, but also small variations in the

relative concentration (%) of FA from derivatized tomato

seed oil samples were registered. An increasing tendency

of concentration of polyunsaturated FA (i.e. C18:2) was

remarked when a reduced extraction time (1–2 percola-

tions) with petroleum ether was used.

The exceptions were C18:1 with a decreasing tendency

from 20.9 % (when diethyl ether was used) to 18.2 %

(when petroleum ether was used) and C18:2 with a

decreasing tendency from 56.8 % (for extended time of

extraction with diethyl ether) to 47.8 % (for extended time

of extraction with petroleum ether).

By increasing the contact surface between milled tomato

seeds (with granularity from 1.5 to \0.5 mm) and the

solvent used for extraction, a slight decrease trend was

noticed for C18:1 and C18:2. An increasing trend was

remarked for all the other FA (expressed in FAMEs) from

derivatized tomato seed oil samples, the most significant

variation was for C18:0 (from 18.2 up to 24.8 %).

A slight increase of the concentration of unsaturated FA

composition (C18:1 and C18:2) was revealed using diethyl

ether for extraction of the tomato seed oil and high gran-

ularity of tomato seeds.

Very interesting results were obtained for the variation

of the absolute concentration (mg/mL) of FAMEs with the

extraction parameters.

When diethyl ether and petroleum ether were used for

extraction of tomato seed oil, a slight variation of FAMEs

concentration (mg/mL) was noticed (Table 2).

An increasing tendency for all analyzed FA was

remarked when petroleum ether was used for extraction,

in comparison with the samples obtained by diethyl ether

extraction. The extraction of C18:2 using diethyl ether as

solvent conducts to a lower absolute concentration of

35 mg/mL in comparison with the petroleum ether case.

By increasing the contact surface between the milled

tomato seeds (with granularity from 0.5–1.5 mm to

\0.5 mm) and the solvent used for extraction, an

Ta

ble

2T

he

abso

lute

con

cen

trat

ion

(mg

/mL

)o

fth

eF

Afr

om

tom

ato

seed

oil

extr

acts

Co

de

C1

4:0

C1

6:1

C1

6:0

C1

7:0

C1

8:0

C1

8:1

C1

8:2

C1

8:3

C2

0:0

DE

E0

.08

±0

0.0

0.0

11

1.2

0.5

80

.08

±0

.01

0.3

0.0

21

2.7

0.7

13

4.7

±1

.72

1.5

0.0

90

.26

±0

.04

PE

10

.05

±0

.01

0.2

0.0

64

.08

±0

.23

0.0

00

.13

±0

.03

2.4

0.1

82

0.8

0.8

60

.75

±0

.05

0.0

0.0

1

PE

20

.10

±0

.02

0.3

0.0

46

.29

±1

.27

0.0

00

.21

±0

.04

4.2

0.7

53

2.3

5.0

71

.41

±0

.36

0.1

0.0

4

PE

40

.12

±0

.04

0.3

0.1

58

.39

±4

.23

0.0

0.0

20

.33

±0

.20

5.5

2.6

13

9.8

15

.73

1.8

0.9

90

.15

±0

.05

PE

60

.24

±0

.01

0.5

0.0

31

9.2

0.6

60

.11

±0

.01

0.8

0.0

41

4.1

0.3

53

7.2

±1

.71

4.9

0.1

50

.43

±0

.01

MM

PE

0.0

0.0

20

.03

±0

9.4

1.2

60

.06

±0

.01

0.2

0.0

31

0.7

1.4

13

0.0

3.2

1.1

0.1

60

.16

±0

Res

ult

sar

ep

rese

nte

das

aver

age

of

du

pli

cate

s

Table 3 Karl Fischer water titration results for tomato seed oil

extracts

Code v1 (lM/s) v2 (lM/s) V/m (mL/g) W (%)a

DEE 10.01 0.46 ± 0.12 0.08 ± 0.01 0.08

PE1 7.97 ± 0.64 0.54 ± 0.03 0.06 ± 0.01 0.06

PE2 6.12 ± 1.67 0.48 ± 0.13 0.07 ± 0.01 0.06

PE4 5.37 ± 0.32 0.41 ± 0.08 0.05 ± 0.01 0.05

PE6 8.90 0.29 ± 0.16 0.07 ± 0.01 0.06

MMPE 2.78 ± 0.56 0.42 ± 0.08 0.04 ± 0.00 0.04

Results are presented as average of triplicatesa Standard deviation \0.01 for all the analyzed samples

J Mater Cycles Waste Manag

123

Page 5: Utilization of seeds from tomato processing wastes as raw material for oil production

increasing trend of all the analyzed FA concentration was

measured. The concentration of the main FA (C18:2,

30 mg/mL) from tomato seed oils was reduced using

mechanically milled tomato seeds with granularity in the

range of 0.5–1.5 mm.

By increasing the number of percolations used for

extraction of tomato seed oil, an increasing tendency of the

FA absolute concentration from the derivatized tomato seed

oil samples was registered. Thus, the absolute concentration

of C18:2 increases with the increasing percolations,

from 20.8 mg/mL, in the case of one percolation, to

38–40 mg/mL, for 4–6 percolations. Using petroleum ether

for extraction of tomato seed oil, a high granularity of milled

tomato seeds (obtained using electric mill,\0.5 mm) and a

high number of percolations led to obtain a high absolute

concentration of FA in the final derivatized extracts of

tomato seed oils.

KFT for determining the water traces from tomato seed

oil

The water content of oily samples is an important

parameter for the quality and stability of these products.

Different methods can be used for water analysis, but

KFT method seems to be more appropriate for this type

of samples due to the possibility to determine only

water (not other volatile substances) in very low

concentration.

As shown in Table 3, the water content of tomato seed

oil samples was in the range of 0.04–0.08 %, the highest

concentration was obtained for tomato seed oil extracted

with diethyl ether (0.08 %), and the lowest concentration

was for the sample obtained from mechanically milled

tomato seeds (0.04 %). All other samples had a water

concentration of 0.05–0.06 %, without significant variation

with the number of percolations.

Fig. 1 The normalized KFT volume (V/m, mL/g) versus time (s) plot

for tomato seed oil obtained by diethyl ether extraction (triplicate

samples, DEE1, DEE2, DEE3)

Fig. 2 The normalized KFT volume (V/m, mL/g) versus time (s) plot

for tomato seed oil obtained by petroleum ether extraction (mechan-

ically milled seeds) (triplicate samples, MM1, MM2, MM3)

Fig. 3 The normalized KFT

volume (V/m, mL/g) versus time

(s) plot for tomato seed oil

obtained by petroleum ether

extraction (different

percolations)

J Mater Cycles Waste Manag

123

Page 6: Utilization of seeds from tomato processing wastes as raw material for oil production

The highest concentration (0.08 %) of water content for

the samples extracted with diethyl ether (in comparison

with the sample extracted with petroleum ether) can be due

to the physical properties of the solvents: the water has a

very low solubility in petroleum ether in comparison with

the diethyl ether, where the water solubility is about 10 %

[19].

The water reaction rate can be an important indicator

for the type of water molecules from the liquid or solid

samples. In the case of tomato seed oil samples, only one

pseudo linear range (generally 10–40 s) in the KFT pro-

cess [titration volume weighted to the sample mass (V/m,

mL/g) versus time (s); see Table 3 for the final V/m

values] can be observed. A second range corresponding to

the normal KFT process (the drift range) can also be

observed.

The water molecules react with a rate of 3–10 lM/s

(which means micromoles/liter/second) in the KFT pro-

cess, with a highest rate of 10 lM/s for DEE samples

(pH 6.23, g = 22.7 mm2/s, standard deviation \0.01)

(Fig. 1).

The lowest reaction rate 3 lM/s (Fig. 2) was obtained

for oil samples isolated from mechanically milled tomato

seeds (MM), granularity in the range of 0.5–1.5 mm (pH

6.15, g = 23.4 mm2/s, standard deviation \0.01).

The number of percolations does not have a significant

influence on the reaction rate of water molecules. In Fig. 3

is presented the normalized KFT volume (V/m, mL/g)

versus time (s) plot for tomato seed oil obtained by

petroleum ether extraction with 1, 2, 4, and 6 percolations.

The water reaction rate values are in the range of

5.4–8.9 lM/s, but no variation with the extraction time was

observed.

Conclusions

Based on the presented results, the following conclusions

can be drawn: (1) tomato seeds from tomato processing

waste are valuable sources of edible nutritive oil that con-

tains a relatively high amount of x-6 essential FA (C18:2).

(2) FA composition of Romanian tomato seed oil is similar

with other results reported in literature. Regarding the type

of solvent used for extraction of the tomato seed oil, we can

conclude that small variations in the absolute concentration

of FA from derivatized tomato seed oil samples were reg-

istered. An increasing tendency of the FA absolute con-

centration in the derivatized tomato seed oil samples with

the number of percolation used for extraction was

remarked. An increasing trend of the concentration of all

FA was reported when the surface between tomato seeds

milled and solvent used for extraction has been increased.

(3) The water reaction rates in the KFT process significantly

depend on the solvent type (less hydrophobic solvent con-

ducts to a higher KFT water reaction rate) and the granu-

larity of the raw tomato seed powder used for extraction, but

no correlation with the FA composition of the tomato seed

oil was observed. Extraction time does not influence the

water content and has a very low influence on the water

reaction rate of all analyzed samples.

Acknowledgments This work was partially supported by the

‘‘Doctoral Studies for Training in Research (FOR-CE)’’ Program,

POSDRU/CPP107/DMI1.5/S/80127, co-financed by the Structural

Funds of the European Union, selected from the Sectoral Operational

Programme Human Resources Development 2007–2013. The authors

would like to thank Professor Heinz-Dieter Isengard from Hohenheim

University, Germany, for the help in the Karl Fischer water titration.

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