Обучение по природни науки и върхови технологии

Експерименти в природните науки

DETERMINATION OF VITAMINS B AND C IN THE BIOMASS GROWN ON THE OLIVE MILL WASTEWATER IN SYRIA BY HPCL METHOD

Резюме. The study includes the results of the pH effect of the extraction solution on water-soluble vitamins in the biomass that grown on the olive mill wastewater (resulting from Syrian olive presses) diluted by urea solutions (4%) 75:25 (OMW; Urea 4%) and grafted with Geoterichum hypha. The vitamins determined by high performance liquid chromatography (HPLC) after extracted it in different pH solutions; Phosphate solution pH = 7, Acetic acid solution 2% pH =2.6 and Sodium hydroxide solution 0.1N pH = 12. The results showed that B1, B3, B6, B7, B9 and C were found in the biomass in different percent amount, according to the extraction solution, but no vitamin B2 was present. .In the pH = 7 the percentage of vitamins in biomass was B6 = 0.006%, B7 = 0.11% and B9 =0.01%. In the acidic medium at pH = 2.6, the percentages of vitamins were B3 = 0.005%, B6 = 0.03%, B7 = 0.45%, B9 = 0.003% and C = 0.025%. In the alkali medium the percentages were as follows: B1 = 0.28%, B7 = 0.03% and B9 = 0.04%.

Ключови думи: olive mill wastewater; vitamins in biomass

Introduction World olive oil production is estimated to around 2.9 million tons a year as Table 1. The EU countries alone produce 72 – 75 % of the world production and the Middle East countries produce 15 – 20% and the other countries about 7 – 10% (Malorgio & Felice, 2014). Extraction process yields oil (which accounts for 20 % of the total mass) and two by-products: a solid residue (30 % of the total), and a black wastewater (50 % of the total) called olive mill wastewater (OMW) (Martin et al., 1991). OMW is an important polluter due to dark colour and high concentration of organic and phenolic compounds, which make OMW toxic and resistant to biological degradation (Mekki et al., 2007). The organic load of OMW, expressed as chemical oxygen demand (COD; range 80 g L-1 to 200 g L-1) and biochemical oxygen demand (BOD; 50 g L-1 to 100 g L-1) is 200 to 400 times higher than in a typical municipal sewage (Cossu et al., 1993). The organic fraction includes sugars, tannins, polyphenols, polyalcohols, pectins, and lipids. The phenolic fraction is recalcitrant to biodegradation and is responsible for several biological affects including phytotoxicity and antibiosis (Dragičević et al., 2010).

Table 1. World olive oil production (Malorgio & Felice, 2014)

CountriesArea(103ha) Production(103tons) Consumption(103tons) Exports(103tons) European Union5,0002,161.11,876.1419.7Tunisia1,850156.736.0132.0Turkey800144.2110.725.4Morocco950105.880.012.0Syria700152.0114.423.5Jordan13526.124.51.6Argentina10022.35.317.0Other465166.3679.336.8Total100002,934.42,926.3669.5

The number of olive presses in Syria reached 841, producing approximately 800 tons of liquid waste per year, which is a real environmental problem because polluted chemicals in soil and groundwater occur (Kholani & Malo, 2012).

The problem of disposing of olive mill wastewater (OMW) remains unresolved, although, there are several attempts (Di Lecce et al., 2014). Some of these methods used to treat OMW from their chemical components (as compounds harmful to the environment) are both chemical methods and physicochemical methods: filtration of magnetic nanoparticles (Nassar et al., 2014); microfiltration membrane technology (Petrotos et al., 2014); biodegration treatment of olive mill wastewater by non-conventional yeasts (Gonçalves et al., 2009); biodegradation treatment through Trichosporon cutaneum and Geotrichum candidum (Dragičević et al., 2010); biodegradation treatment by thermophilic bacteria (Al-Qodah et al., 2015).

Some researchers investigated the biomass resulting from biodegradation treatment on OMW medium and found a high quantity of proteins which could be used in animal feeds (Kholani & Malo, 2012). This study includes the determination vitamins B and C in the biomass that grown the OMW diluted with 4% urea solution. Vitamins are complex organic substances found in small quantities in different foods, which should be presented in other nutrients to maintain vital functions. The vitamins are in two parts: ones are dissolved in fat and others are dissolved in water and these groups of vitamins play an important role in all the enzymes necessary to complete the various biological processes. The body cannot produce vitamins so it is expected the food to supply them in the necessary quantities (Malo et al., 2011).

Table 2. Chemical structure and general characteristics of water-soluble vitamins

VitaminStructureGeneralcharacteristicsThiamine, orvitamin B1NNN+SNH2OHColorless anddissociate withlight and heatNiacin, or nicotinicacid or B3NOOHColorless anddissolve inhot water anddissociate in alkalipHRibovlavine, or B2NNNHNOHOHOHOHOCH3CH3Oyellow colordissolves in thealkaline mediumPyridoxine orpyridoxol orvitamin B6, NOCH3OPOHOHOColorless
Biotin or vitaminB7 or vitamin H orcoenzyme RNHNHSHHOCOOHColerlessFolate, or folic acidor vitamin B9NNHNNNHNH2NHCO2HCO2HOOyellow colordissolves in thealkaline mediumAscorbic acid orVitamin COOOHOHOHOHHColorless, stable in theacidic medium, dissipated byheat and lightand ultravioletradiation

Materials and methods

Instrumentation and chemicals

High performance liquid chromatograph (Knauer, Germany), centrifuge (Harmonic series, Taiwan). Organic and inorganic solvents of HPLC grade such as methanol and phosphoric acid were obtained from Merck (Germany). All water soluble vitamins: thiamin, riboflavine, nicotinic acid, pyridoxine, biotin, folic acid and ascorbic acid from Laboratory Rasayan; sodium hydroxide and acetic acid from Panreac (Spain).

Samples collection and preparation: OMW collect

The OMW was collected from a local contemporary (Syria). The press was close to Damascus in countryside called (Adiliya), it collected immediately after the press and were saved by heating them 70Co to inhibit enzymes from the microorganisms (Kholani et al., 2012). The samples were placed in sealed plastic containers and placed in refrigerator 4Co(Takriti et al., 2009).

Preparation of the bio-material

Olive fruits were washed, and the knife was washed, then immersed in water and left in the room temperature for a week (Kholani et al., 2012). And then took the Geotrichum threads of Hypha (Ashkar, 2010) (Fig. 1). The Geotrichum Hypha was growed for seven days at 28Co and in a medium containing 1.6 g/L monohydrogenate phosphate, 0.025 g calcium chloride, 0.5 g ammonium nitrate, 0.4 g mono-potassium phosphate, 0.2 g magnesium sulphate and 0.0025 g ion(III) chloride and 10 g sucrose (Chandra et al., 2011).

Figure 1. Microscopic checking for the Geotrichum threads of hypha

Figure 2. The biomass that growth on medium containing: monohydrogenate phosphate, calcium chloride, ammonium nitrate, mono-potassium phosphate, magnesium sulphate and ion(III) chloride and sucrose

Preparation of the solutions

Urea 4 %(w/V): dissolve 4g Urea in 10ml ddH2O; Buffer phosphate 0.1M pH=7: dissolve 0.356 g Na2HPO4.2H2O in 10ml ddH2O(A), dissolve 0.276 g NaH2PO4 in 10ml dd H2O (B), add 3.6ml (A) to 1.4ml (B) then 5ml ddH2O; sodium hydroxide 0.1N pH=12: dissolve 0.04g NaOH in 10 ml ddH2O; acetic acid 2% (v/v) pH= 2.6: add 2ml acetic acid to 8ml ddH2O; Vitamins standard solution: the aqueous stock solution (1mg/ml) of each vitamin was prepared every week, kept in the refrigerator, in an aluminum foil, protected from light; and working standards (in the range of 0.05 – 0.5mg/ml), were used daily by appropriate dilution of the stocks. The standard curves were made by running min. 6 different concentrations of each vitamin on HPLC system (Parlog et al., 2008).

Chromatographic HPLC protocol

For the separation of the six vitamins B and ascorbic acid, a Vertex plus Column 250x4.6mm Eurospher 100-5 C18 was used at ambient temperature. The mobile phase consisted of (A) phosphoric acid: water (0.01:100), (B) methanol, at a flow rate 0.8ml/min, UV/Vis, (230, 265,280) nm, the injection volume was 20 microliter, a multi-step gradient was optimized as Table 3.

Table 3. Gradient illusion program that used for vitamin separation

A%B%Flow rate (ml/min) Rentation time (min) 90100.8-----90100.81010900.830001000.83590100.84090100.860

Biomass sample preparation

The hypha was added to OMW diluted by aqueous urea 4%(75:25) and kept for seven days at 28Co. the Biomess collected and washed by water then kept dry at room temperature (Kholani et al., 2012) (Fig. 3).

Figure 3. The biomass that growth on OMW diluted by aqueous urea 4%(75:25) and kept for seven days at 28Cº

Extraction vitamins from the biomass

Two methods that have been relied upon by researchers have been combined (Parlog et al., 2008; Daghestani & Al-Bahra, 2003).

The samples were either analyzed as buffer phosphate extract or after hydrolysis. The samples hydrolysis was done in Sodium Hydroxide (NaOH) 0.1N (alkaline Hydrolysis) or in 2 % acetic acid (CH3COOH).

The procedure includes: weigh 1 g of the biomass and crush in a porcelain bowl, divide the powder into three equal sections in three plastic test tubes and in each place 0.3 g of them and add to each tube as follows: first tube: 5 ml 0.1M phosphate buffer; second tube: 5 ml of 0,1 N sodium hydroxide; third tube: 5 ml of 2 % acetic acid. The three tubes were placed on a 400 rpm magnetic stirring for four hours at a temperature 30Co, then centrifuged (10000 rpm, 10 min, 20Co), removed the solid mass and collected the supernatant liquid then precipited protein by acetone after adjusted pH =5, kept the tubes in refrigerator to second day, centrifuged (10000 rpm, 5min, 20Co), then adjusted the supernatant to pH=7 by sodium hydroxide and finally transferred the abstract to three glass tubes sealed and covered with aluminum foil to prevent take apart vitamins by light until they were analyzed by the HPLC.

Results and discussion

HPLC Separation of vitamins using pure standards

At first, the HPLC analysis was performed using individual solutions, and then mixed standards as presented in Fig. 4. We selected the most suitable absorption wavelength in order to obtain their simultaneous detection since their spectral properties differ very seriously, the peak intensity was different at 260nm, the highest being for folic acid then thiamin and lowest B7 (or the Biotin). Then we saved the retention time for each vitamins as shown in Table 4.

Table 4. Specific retention time for the seven vitamins

Retention timeVitamin type3.18B14.05C4.48B35.45B621.4B923.32B227.7B7

Figure 4. HPLC chromatogram of a mixture of pure standards of vitamins B1, B2, B3, B6, B7, B9, C

The standard chains of each vitamin were studied at the appropriate wavelengths (concentration in terms of area) (Fig.5). Let us take advantage of them later by setting the amount of vitamin according to the area of the appropriate rectal equation.

Figure 5. The standard chains of B1, B2, B3, B6, B7, B9,C (concentration mg/ml in terms of area)

HPLC analysis of water- soluble vitamins from biomass that growing on OMW: urea 4% and extraction the vitamins with phosphoric buffer pH=7

Fig. 6 presents the HPLC chromatogram of the biomass that growing on OMW: urea 4%, extracted in phosphoric buffer solution at 30Co. We can identify vitamins B6, B7, B9 and determine the percent amount of them in the biomass depending on standard chain end retention time as shown in Table 5.

Table 5. Percent amount vitamin amounts in the biomass depending on standard chain and retention time

Percent amount %AreaRetention timeVitamin type0.0063605745.5417B60.015554421.65B90.119873127.317B7

Figure 6. HPLC chromatogram of free vitamins from biomass extraction in phosphoric buffer

HPLC analysis of water- soluble vitamins from biomass that growing on OMW: urea 4% and extraction the vitamins with acetic acid pH=2.6

Fig. 7 presents the HPLC chromatogram of the biomass that growing on OMW: urea 4% extracted in acetic acid solution at 30CopH=2.6. We can identify vitamins B3, B6, B7, B9, C and determine the percent amount of them in the biomass depending on standard chain end retention time as shown Table 6.

Table 6.1. Percent vitamin amounts in the biomass depending on standard chain and retention time

Percent amount %AreaRetention timeVitamin type0.025662004.267C0.005219574.783B30.03146135.483B60.003794421.067B90.4537101627.483B7

Figure 7. HPLC chromatogram of free vitamins from biomass extraction in acetic acid pH=2.6

HPLC analysis of water- soluble vitamins from biomass that growing on OMW: urea 4% and extraction the vitamins with hydroxide sodium pH=12

Fig. 8. presents the HPLC chromatogram of the biomass that growing on OMW: urea 4%, extracted in hydroxide sodium solution at 30Co pH=12. We can identify vitamins B1, B7, B9 and determine the percent amounts of them in the biomass depending on standard chain end retention time as shown Table 7.

Table 6.2. Percent vitamin amounts in the biomass depending on standard chain end retention time

Percent amount %AreaRetention timeVitamin type0.2818454663.567B10.0411430821.5B90.033284827.417B7

Figure 8. HPLC chromatogram of free vitamins from biomass extraction in hydroxide sodium pH=12

Table 7. Percent vitamin amounts in the biomass depending on pH extraction

C %B9 %B7 %B6 %B3 %B2 %B1 %pH extraction0.0250.0030.450.030.005--------pH=2.6----0.010.110.006-------------pH=7----0.040.03------------0.28pH=12

Conclusions

In this work we optimized the protocols for HPLC separation of seven water soluble vitamins: thiamin, riboflavin, nicotinic acid, pyridoxine, biotin, folic acid and ascorbic acid as pure standard solution, using an original and optimized protocol.

Table 7 explains the conclusion of this study: same vitamins were analyzed differently, as phosphoric buffer extract or as acid or alkaline hydrolyzed extracts. The phosphoric buffer extracts contain only small quantities of free vitamins B6, B7, B9 but B6, while the acid hydrolyzed extract contains five vitamins B3, B6, B7, B9 and C and the highest concentration is to B7 comparative with other vitamins and to other pH extract. It should be noted that ascorbic acid or vitamin C does not appear in other extraction medium.

Finally, the alkaline extract contained three vitamins B1, B7 and B9 and the highest concentration was to B1 comparative with other vitamins and to other pH extract. It should be noted that B1 or thiamine does not appear in other extraction medium. Generally, we cannot depend the specific pH to extract vitamins, but each time we should extract on different pH, because some vitamins appear in the acidic pH and the other with an alkaline pH and other on pH=7. Although some vitamins are extracted in the three circles but their concentration varies from one medium to another.

REFERENCES

Al-Qodah, Z., Al-Shannag, M., Bani-Melhem, K., Assirey, E., Alananbeh, K. & Bouqellah, N. (2015). Biodegradation of olive mills wastewater using thermophilic bacteria. Desalination & Water Treatment, 56, 1908 – 1917.

Ashkar, K. (2010). Fungi theoretical part. Publications of Damascus University, Faculty of Science, pp. 286 – 288.

Chandra, R., Yadav, S., Bharagava, R.N. & Rai, V. (2011). Phenol degradation by Paenibacillus thiaminolyticus and Bacillus cereus in axenic and mixed conditions. World J. Microbiology & Biotechnology, 27, 2939 – 2947.

Cossu R., Blakey, N, Cannas, P. (1993). Influence of codisposal of municipal solid waste and olive vegetation water on the anaerobic digestion of a sanitary landfill. Water Sci. & Tech., 27, 261 – 271.

Daghestani, M. & Al-Bahra, M. (2003). The chemical compositions of beans and beans shell. Damascus Univ. J. Basic Sci., 19,.43 – 61.

Di Lecce, G., Cassano, A., Bendini, A., Conidi, C., Giorno, L. & Toschi, T.G. (2014). Characterization of olive mill wastewater fractions treatment by integrated membrane process. J. Sci. Food & Agric., 94, 2935 – 2942.

Dragičević, T.L.S., Hren, M.Z., Gmajnić, M., Radman, S., Kungulovski, D., Kungulovski, I., Cvek, D., Frece, J., Markov. K. & Delaš, F. (2010). Biodegradation of olive mill wastewater by Trichosporon cutaneum and Geotrichum candidum. Arch. Ind. Hygiene & Toxicology, 61, 399 – 405.

Gonçalves, C., Lopes, M., Ferreira, J.P. &Belo, I. (2009). Biologicaltreatment of olive mill wastewater by non-conventional yeasts. Bioresource Tech., 100, 3759 – 3763.

Kholani, E. & Malo, A. (2012). Nutrient resources rich in proteins production by using of olive mill waste water. Damascus Univ. J. Basic Sci., 12, 346 – 360.

Malo, A., Al-Bahra, M. & Al-Azmeh, H. (2011). Structural biochemistry. Publication Damascus University, Faculty of Science, pp. 286 – 288.

Malorgio, G. & Felice, A. (2014). Trade and logistics: the fruit and vegetables industry (pp. 149 – 171). In: Lacirignola, V. (Ed.). MediTERRA: logistic and agro-food trade: a challenge for the Mediterranien. Paris: Presses de Sciences.

Martin, A., Borja, R., Garcia, I. & Fiestas, J.A. (1991). Kinetics of methane production from olive mill wastewater. Process Biochem., 26, 101 – 107.

Mekki, A., Dhouib, A. & Sayadi, S. (20070. Polyphenols dynamics and phytotoxicity in a soil amended by olive mill wastewaters. J Environ. Management,84, 134 – 140.

Nassar, N.N., Arar, L.A., Marei, N.N., Abu Ghanim, M.M., Dwekat, M.S. & Sawalha, S.H. (2014). Treatment of olive mill based wastewater by means of magnetic nanoparticles: decolourization, dephenolization and COD removal. Environ. Nanotech., Monitoring & Management, 1 – 2, 14 – 23.

Parlog, R.M., Nicula, A., Nicula, A.T. & Socaciu, C. (2008). The optimization of extraction and HPLC analysis of vitamins B from yeast products. Bull. Univ. Agric. Sci. & Vet. Med. Cluj-Napoca (Agriculture) , 65, 323 – 328

Petrotos, K.B., Lellis, T., Kokkora, M.I. & Gkoutsidis, P.E. (2014). Purification of olive mill wastewater using microfiltration membrane technology. J. Membrane & Separation Tech., 3, 50 – 55.

Takriti, S., Al-kaid, A. & Ibrahem, S. (2009). Radiation processing of the olive-press waste waters for detoxifying the water from organic pollutants. Syrian Arab Rebablic Atomic Energy Commission: Report, pp. 1 – 11.

Година XXVII, 2018/2 Архив

стр. 244 - 257 Изтегли PDF