DECOLOURISATION OF AZO-BASED FOOD COLOURANTS
(Carmoisine and Ponceau 4R) BY Escherichia coli.
1
N. C. Oforka and 2N. A. Oranusi*1DEPARTMENT OF PURE AND INDUSTRIAL CHEMISTRY,
2
DEPARTMENT OF MICROBIOLOGY, UNIVERSITY OF PORT HARCOURT, NIGERIA.
ABSTRACT
Decolourisation of azo-based food colourants (Carmoisine and Ponceau 4R) by Escherichia coli isolated from human feaces was investigated. Decolourisation was assessed by changes in optical density of culture supernatant and total viable count in media containing the colourants as sole source of carbon and energy. Decrease in optical density was accompanied by increase in total viable count during incubation. Percentage decolourisation of carmoisine was 80% and 75% under aerobic and anaerobic cultivation respectively. The values in Ponceau 4R containing medium were 62.5% and 60% under aerobic and anaerobic cultivation respectively. The potential health risk associated with decolourisation intermediates (aromatic amines) is discussed.
Key words: Food Colourants, Decolourisation, Escherichia coli.
INTRODUCTION
Azo dyes are the largest class of synthetic dyes with the greatest variety of colours. At least 3,000 different varieties of azo dyes are extensively used in the textile, paper, food, cosmetics and pharmaceutical industries (Chen et al., 1999). Azo dyes are largely non-toxic, however, decolourisation of azo dyes by reductive cleavage of the azo bond (chromophore) produces aromatic amines as intermediates. Aromatic amines are toxic, mutagenic and carcinogenic to humans and other animals (Cartwright, 1983; IARC, 1982; Brown and Devito, 1993; Levine, 1991; Ganesh, 1992).
Cleavage of azo bond is mediated by azoreductases. Azoreductases are synthesized by microorganisms (Chen et al., 1999; Gary et al., 1994; Chinwetkitvanich et al., 2000; Rasso-Flores et al., 1997; Brown and Labourer, 1983). Degradation of azo dyes by human intestinal microflora has been reported (Fatemeh et al., 1990 and King-Thom et al., 1978). These studies were carried out in complex media involving consortium of bacteria. The specific organism of the intestinal macroflora participating in azo dye reduction is poorly understood.
Most azo dyes are used as food colourants. The aims of this study were to isolate, identify some intestinal bacteria and assess the decolourisation potential of azo-based food colourants commonly used in Nigeria by the isolates. This study focused on Escherichia coli and food colourants (Carmoisine and Ponceau 4R).
MATERIALS AND METHODS
AZO DYES
Liquid formulations of Carmoisine and Ponceau 4R (Rayner & Co. Ltd., England) were purchased from a supermarket in Port Harcourt, Nigeria. They are food colourants commonly used in Nigeria: Stock solution of each dye was prepared by membrane filteration (pore size 0.2μm, Acrodisc). Fig. 1 shows the chemical structure of the dyes.
Medium
The basal medium contained (gL-1): NaNO3 0.3, MgSO4 . 7H2O 0.42, KCl 0.29, K2HPO4 1.27, KH2PO4 0.85, NaNO3 0.42 and deionised water 1,000ml. Agar No. 1 (Oxoid) was added at 1.5% (w/v) to prepare solid medium. After sterilization and cooling, 0.5ml of stock solution of Carmoisine or 0.3ml of Ponceau 4R was added to the basal medium. Medium which contained Carmoisine was coded MSC while, MSP was for medium which contained Ponceau 4R.
Isolation and identification
One gram of freshly voided human feaces was sterially diluted (10-1 10-3) in physiological saline A loopful of each dilution was inoculated by streaking onto duplicate set of MacConkey agar plate. The plates were incubated at 37oC for 24 48h.
Pink colonies, which developed were picked and inoculated into 10ml MacConkey broth and incubated at 37oC for 24h. Duplicate set of Eosine
CARMOISINE
Fig. 1 Molecular structures of the azo dyes (Ponceau 4R & Carmoisine
Methylene blue agar (EMB) plates were each inoculated with a loopful of the culture. Incubation was at 37oC for 24 48h. Blue/black colonies surrounded by metallic sheen were picked and purified by repeated subculture and Gram stained. Colonies which were distinctly Gram negative and rod-shaped were used for various identification tests.
Various tests (motility, presence/absence of spore, urease, citrate utilization, hydrogen sulphide production, MRVP, catalase, oxidase, indole, starch hydrolysis and fermentation of various sugars) were carried out according to the methods of Cruickshank et al. (1980) and Holts et al. (1994). Based on the results of these various tests, and with reference to Bergeys Manual of Determinative Bacteriology, the isolate was identified as Escherichia coli (E. coli). Stock cultures were maintained on EMB slants in a refrigerator at 4oC.
STANDARD INOCULUM
Colonies were picked from the slants and inoculated into 10ml MacConkey broth. Incubation was at 37oC for 24h.
SCREENING OF E. COLI TO DECOLOURISE THE DYES
BROTH CULTURE:
Duplicate set of 250ml Erlenmeyer flasks each containing 25ml of either MSC or MSP were inoculated with 1ml of a 24h MacConkey broth culture. Two sets of controls were also set up: positive control consisted of duplicate flasks inoculated with 1ml of heat-treated cells and negative controls consisted of uninoculated flasks.
The flasks were incubated at 37oC with shaking and observed daily for decolourisation of medium (evidence of degradation) and increase in turbidity (evidence of growth). Increased turbidity and decolourisation of medium were observed in all the flasks which were inoculated with viable cells from the second day of incubation. These changes reached their peak on the fifth day. There was neither decolourisation nor turbidity in the control flasks.
SOLID MEDIA
A loopful of the standard inoculum was streaked onto duplicate set of either MSC or MSP agar plates. The plates were incubated at 37oC and observed daily for appearance of zones of clearing (decrease in colour intensity) around the colonies. Controls consisting of duplicate set of uninoculated MSC or MSP agar plates were also set up. Zones of clearing were observed in all the inoculated plates after four days of incubation. The intensity of colour of the medium remained the same in the control plates. The results obtained in the screening tests showed that the organism degraded the dyes.
KINETICS OF GROWTH AND DECOLOURISATION IN SUBMERGED CULTURE
CARMOISINE
Triplicate set of 250ml Erlenmeyer flasks each containing 95ml of MSC broth was inoculated with 5ml of standard inoculum (ca. 106 cfu ml-1). The flasks were incubated at 37oC with shaking. Controls consisted of triplicate set of uninoculated medium. Growth and decolourisation were monitored by determination of total viable count (TVC) and decrease in optical density (O.D.) of the culture supernatant respectively. Changes in pH were also monitored.
PONCEAU 4R
The set up was same as for Carmoisine except that the medium was MSP broth.
DETERMINATION OF TOTAL VIABLE COUNT (TVC)
One millimeter was aseptically withdrawn at regular intervals from each flask and serially diluted (10-1 to 10-6) in 9ml physiological saline. One millimeter of appropriate dilution was inoculated into duplicate set of nutrient agar plates by the pour plate method. Plates were incubated at 37oC for 24 48h and the number of colonies which developed counted. Results are expressed as colony-forming-unit per ml (CFU ml-1).
Anaerobic Cultivation
Three loopfuls of standard inoculum (ca.1.2 x 106 CFU ml-1) was inoculated into either 10ml MSC of MSP medium contained in triplicate set of test tubes. The tubes were immediately overlaid with sterile vaseline. Incubation was at 37oC for 7days in an Anaerobic jar.
After incubation the broth was centrifuged at 6,000 rpm for 30 min. The optical density of the supernatant was determined spectrophotometrically (Jenway 3100). The pH was also determined.
OPTICAL DENSITY (O.D.) DETERMINATION
One millimeter was ascetically withdrawn from each flask and pooled (3ml). The pooled sample was centrifuged at 6,000 rpm for 30 min in a bench centrifuge (Baird & Tatlock, England). The resulting supernatant was withdrawn and the O.D. determined spectrophtometrically (Jenway 3100) at λmax for each dye. Results are expressed as percentage dye decolourisation.
% dye Decolourisation = OD initial -OD sample x 100
OD initial 1
pH DETERMINATION
The pH of the above supernatant was determined using pH meter (Mettler Delta 3400).
AZOREDUCTASE ACTIVITY IN CULTURE SUPERNATANT
Unless otherwise stated azoreductase activity in culture supernatant was determined as follows: All procedures were carried out at 4oC and filteration was by membrane filteration (0.2
μm pore size Acrodisc). Cultures were grown as for Kinetics of Growth and Decolourisation experiment above for 7 days. The culture broth was filtered. The protein (enzyme) in the supernatant in the filterate was precipitated with 70% (w/v) ammonium sulphate at 4oC for 24h. The resulting precipitate was recovered by filteration and dissolved in 10ml of phosphate buffer at pH 7.0 (determined from preliminary experiment). The enzyme solution was concentrated and desalted by dialysis (Medical International Ltd., Dialysis Tubing, Visking) against several changes of deionised water and sterilized by filteration.The reaction mixture consisted of 0.05ml of Carmoisine or 0.04ml of Ponceau 4R and either 1ml of crude enzyme solution (obtained prior to addition of ammonium sulphate) or 1ml of ammonium sulphate precipitated enzyme solution. The optical density of the reaction mixture was 0.5 units. Incubation was at 37oC for 20 min. Controls consisted of 1ml of deionised water instead of enzyme solution. Reaction was stopped by boiling for 20 min. and centrifuging. The optical density of resulting supernatant was determined spectrophotometrically at
λmax for each dye. Results are expressed as percentage decolourisation calculated as before under the conditions of the assay.RESULTS AND DISCUSSION
ISOLATION AND IDENTIFICATION
The isolation procedures with selective media ensured the isolation of the desired organism. The isolate was further purified and identified. The isolate was Gram negative rod and motile. It was positive for catalase, methyl red, oxidase and negative reaction for citrate utilization, hydrogen sulphide production, urease activity, gelatin liquefaction and starch hydrolysis. Fermentation of glucose and mannitol was positive for gas and acid and no gas for lactose and sucrose. The bacterium as tentatively identified as Escherichia coli (E. coli) by reference to Bergeys Manual of Determinative Bacteriology (Holts et al., 1994).
SCREENING FOR DECOLOURISATION
Tables 1 and 2 shows the results obtained on decolourising potential of E. coli. Decolourisation (decrease in colour intensity of the medium) was noticeabe from the second day of incubation in broth culture. On the sixth day decolourisation was intense in medium which contained Carmoisine and moderate in Ponceau 4R medium.
On solid medium decolourisation was slower compared with the broth becoming noticeable on the third day. Decolourisation of azo dyes is attributed to reductive cleavage of azo bond ( N = N ). No decolourisation was observed in the control flasks and plates. The results show that decolourisation was due to metabolic activity of viable and growing cells
Table 1. Screening of E. coli for decolourisation of dyes in broth culture.
|
Time (days) |
||||||||
|
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
|
|
Carmoisine |
- |
+ |
++ |
++ |
++ |
+++ |
+++ |
+++ |
|
Ponceau 4R |
- |
+ |
+ |
+ |
+ |
++ |
++ |
++ |
Table 2. Screening of E. coli for decolourisation of dyes on solid medium.
|
Time (days) |
||||||||
|
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
|
|
Camoisine |
- |
- |
+ |
++ |
++ |
++ |
+++ |
+++ |
|
Ponceau 4R |
- |
- |
+ |
+ |
+ |
++ |
++ |
++ |
Key: - no decolourisation
+ slight decolourisation
++ moderate decolourisation
+++ intense decolourisation
Bacterial have been reported to decolourise azo dyes: Bacillus subtilis (Ziss & Lyberotos, 1998); Proteus mirabilis (Chen et al., 1999); Pseudomonas sp. (Oranusi & Ogugbue, 2002) and Cellulomonas sp. (Oranusi & Ogugbue, 2003).
KINETICS OF GROWTH AND DECOLOURISATION
Figs. 2 & 3 depict the growth profile and changes in optical density (OD) of culture supernatant (decolourisation) when E. coli was cultured on MSC and MSP media respectively. In both medium increase in total viable count (TVC) was accompanied by concomitant decrease in optical density of culture supernatant over time.
In MSC (Fig. 2) TVC was 1.50 x 106 CFU ml-1 on first day and increased steadily to a maximum population density of 6.5 x 109 CFU ml-1 on the seventh day. The culture then remained fairly constant. The OD of culture supernatant decreased from initial value of 0.5 absorbancy unit to 0.10 absorbancy unit (80% decolourisation) on the seventh day.
In MSP medium (Fig. 3) the population density increased from 1.7 x 106 CFU ml-1 on first day to a maximum of 8.70 x 108 CFU ml-1 on the sixth day. The OD increased from 0.40 absorbancy unit on first day to 0.15 units (62.5% decolourisation) on the sixth day. Higher percentage decolourisation (80%) on MSC medium compared to 62.5% on MSP medium may be explained on the number of azo linkage. Carmoisine is a monoazo while, Ponceau 4R is a diazo. The cleavage of single bond in Carmoisine was faster than the double bond in Ponceau 4R.
The dye molecules were the sole sources of carbon and energy in MSC (Fig. 2) and MSP (Fig. 3) media. Aerobic metabolism of azo dyes involves the
Initial reductive cleavage of azo bond followed by ring opening of aromatic moiety of the aromatic amines. The carbon atoms are then utilized as carbon source. The increase in total viable counts (Figs. 2 & 3) show that the dye molecules served as sole sources of carbon and energy. Previous studies (Oranusi and Ogugbue, 2001; 2003, and Chen et al., 1999) reported bacterial utilization of azo dyes as sole sources of carbon and energy under aerobic conditions.
The pH increased from initial pH 7.0 to final pH 7.40 on medium which contained Carmoisine and pH 7.2 on medium which contained Ponceau 4R in aerobic cultures. Under anaerobic cultivation, the pH was 7.30 in MSC medium and 7.10 in MSP medium. The increase in pH to the alkaline range may be due to accumulation of intermediate by-products (aromatic amines) and/or other metabolic products.
ANAEROBIC CULTIVATIONS
Decolourisation was observed when the bacterium was cultured under anaerobic condition. Percentage dye decolourisation was 75% in Camoisine containing medium (MSC) and 60% in medium which contained Ponceau 4R (MSP). No decolourisation was observed in the control flask. Escherichia coli is a facultative anaerobe. The results show that decolourisation could occur in the anaerobic environment of the gastrointestinal tract.
After cleavage of azo bond the component aromatic amines are absorbed in the intestine and may be excreted in urine and/or enter the general circulation (Brown and Devito, 1993). According to Brown and Devito (1993), azo dyes might be toxic only after reductive cleavage of azo bond producing aromatic amines. Aromatic amines have been implicated in cases of bladder cancer in humans, human methemoglobinemia, induced tumors in liver, intestine and urinary bladder in experimental animals (Medvedez et al., 1988 and Kech et al., 1997).
Food colourants are used for aesthetic reasons rather than for their nutritional qualities. The latency of various types of bladder cancer is 20 years. However, cases of bladder cancer have just been reported after few months of ingestion (Cartwright, 1983). Cases of intestinal cancer is more common in industrialized countries (Berg and Howell, 1974; Wynder, 1974) with increasing industrialization, urbanization and increased consumption of foods containing azo dye-based food colourants the potential health risk is a reality. In industrialized countries, the use of food colourants is under strict regulatory control (Houk et al., 1991). In developing economies cases of various forms of human cancer are more common among affluent population (no available data).
This study has demonstrated that E. coli decolourised the azo-based food colourants (Carmoisine and Ponceau 4R) under anaerobic and aerobic conditions. The azo reductase are extracellular and decolourised the dyes. Studies are continuing on other gastrointestinal and urinary bladder microflora which have the potential to decolourise these and other food colourants. The properties of the azo reductases and identification of the aromatic amines are also being investigated.
Acknowledgement
This research was funded by Senate Research Grant, University of Port Harcourt, Port Harcourt, Nigeria. We are grateful to C. J. Ogugbue and A. Sede for technical assistance.
REFERENCES
Berg, T. W. and Howell, M. A. (1974). The geographic pathology of bowel Cancer. Cancer, 34, 807 814.
Brown, D and Labourer, P. (1983). The Degradation of Dyestuffs: Part 1 Primary Biodegradation under Anaerobic Conditions. Chromophore, 12, 397 404.
Brown, M. A. and Devito, S. C. (1993). Predicting azo dye toxicity: Critical Reviews in Environmental Science and Technology. 23, 249 324.
Cartwright, R. A. (1983). Historical and modern epideomological studies on population exposed to N-substituted aryl compounds. Environmental Health Perspectives. 49, 13 19.
Chen, K. C., Huang, W. T., Wu, T-Y and Houng, J-Y (1999). Microbial decolourisation of azo dyes by Proteus mirabilis. J. Industrial Microbol. and Biotech. 23, 686 690.
Chinwetkitvanich, S., Tuntoolvest, M. and Panswad, T. (2000). Anaerobic Decolourisation of Reactive Dyebath Effluents by a Two-Stage UASB System with Tapioca as a Co-substrate. Water Research. 34, 2223 2232.
Clark, E. A. and Aniker, R. (1980). Organic dyes and pigments In Handbook of Environmental Chemistry. Springer Verlag.
Cruickshank, R., Duguid, J. P. and Swan, R. H. A. (1980). Medical Microbiology 11th ed. Publ. English Language Book Society and E. & S. Livingstone, Ltd., Edinburgh.
Fatemeh, R., Franklin, W. and C.E. Ceringlia (1990). Azoreductase Activity of Anaerobic Bacteria Isolated from Human Intestinal Microflora. Appl. and Environmental Microbiology. 56, 2146 2151.
Ganesh, R. (1992). Fate of Azo Dyes in Sludges Masters Thesis. Virginia Polythechnic Institute and State University, p 133.
Gary, A. D., Timm, R. G. and Alexander, V. H. (1994). Azoreductase with the Greening of Instant Chocolate Puddings Appl. Environmental Microbiology. 60, 3027 3029.
Holts, G. J. and Bergey, D. H. (1994). Bergey's Manual of Determinative Bacteriology Vol. 1. Williams and Wikins Co., Baltimore.
Houk, J. M., Doa, M. A., Dezube, M. and Rovinski, J. M. (1991). Evaluation of dyes submitted under the Toxic Substances Control Act new Chemicals Programme. In Colour Chemistry. Elsevier Science Publication Ltd., London, 135 150.
IARC World Health Organisation International Agency for Research on Cancer (1982). Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans: Some Industrial Chemicals and Dyestuffs, Vol. 29. Lyon, France.
King-Thom, C., George, E. F. and Mary, E. (1978). Reduction of Azo dyes by Intestinal Anaerobes. Appl. and Environmental Microbiology, 35, 558 562.
Levine, W. G. (1991). Metabolism of Azo dyes: Implications for Detoxification and Activation. Drug Metabolism Reviews. 23, 253 309.
Medvadez, Z. A., Crowne, H. M. and Medvedera, M. N. (1988). Age related variations of hepatocarcinogenic effect of azo dye (31MDAB) as linked to the level of hepatocyte polyploidization. Mech. Aging Dev. 46, 159 174.
Oranusi, N. A and Ogugbue, C. J. (2001). Degradation of sulphonated azo dyes by Pseudomonas sp. J. Appl. Science and Environmental Management, 5, 13 17.
Oranusi, N. A. and Ogugbue, C. J. (2003). Biodegradation of Azo dyes by Cellulomonas sp. African J. Appl. Zool. and Environmental Biology, 5, 58 63.
Razo-Flores, E., Luijten, M., Donlon, B., Lettinga, G., Field, J. (1997). Biodegradation of Selected Azo dyes Under Methanogenic Conditions. Water Science Technology. 36, 65 72.
Wynder, E. C. and Reddy, (1974). Metabolic epideomology of colorectal cancer. Cancer. 34, 801 806.
Ziss, U. and Lyberatos, G. (1996). Azo dye degradation under anoxic conditions. Water Science Tech. 34, 495 500.