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Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44
© 2015, IJCRCPS. All Rights Reserved 41
INTERNATIONAL JOURNAL OF CURRENT RESEARCH IN
CHEMISTRY AND PHARMACEUTICAL SCIENCES
(p-ISSN: 2348-5213: e-ISSN: 2348-5221)
www.ijcrcps.com
Research Article
BIO DECAFFEINATION-A STUDY ON THE EFFECTS OF BREVIBACTERIUM ON
DIFFERENT SAMPLES OF COFFEE, TEA AND COLA CONTAINING CAFFEINE
J. SUMITHA*, C.RATHNAVEL1
AND T. SIVAKUMAR2
*Research and Development Centre, Bharathiar University, Coimbatore-641 046, Tamil Nadu, India
*PG Department of Microbiology, JBAS College for Women, Teynampet,
Chennai-600 018, Tamil Nadu, India
1
Department of Chemistry, Manonmaniam Sundaranar University, Abhishekapatti,Tirunelveli-627012,Tamilnadu,India
2
Department of Microbiology, Kanchi Shri Krishna College of Arts and Science,
Kilambi, Kanchipuram-631551, Tamil Nadu, India
*Corresponding author
Abstract
HPLC analysis of caffeine was performed in SHIMADZU LC 20 – AD system, and the caffeine compounds were separated on a
C18 column under isocratic conditions with 40% methanol in water at a flow rate of 1.0 ml/min. Compounds eluting from the
column were detected and the peak areas were compared with those obtained with standards of known concentration. The HPLC
analysis of caffeine degradation by Brevibacterium is done by injecting the sample volume of about 20µl HPLC analysis is done
for the sample at different incubation periods with standard caffeine concentration (Known). The sample is analyzed for every
twelve hours of incubation and peak values are obtained. Caffeine concentration is an important parameter to be checked as
excessive consumption of caffeine leads to many health hazards.
Keywords: , Biodecaffeination, Brevibacterium, HPLC.
Introduction
Caffeine
Caffeine is found in about a hundred species of plants,
but the most highly cultivated sources are the coffee
beans, (Coffea arabica or Coffea canephora, variety
robusta), the leaves & leaf-buds of tea (Thea sinensis or
Camellia sinensis), cola nuts (Cola acuminata) and
cocoa beans (Theobroma cacao).Coffee and tea plants
are the major sources of natural caffeine and related
compounds such as theophylline and theobromine
1
. A
very large proportion of the non-alcoholic beverages
used in social settings contain caffeine. The most
important beverages and foods containing caffeine are
coffee, tea, cola nuts, cola drinks, cocoa, and
chocolate. The present study employs different coffee
samples to test the bio-decaffeinating effect. Caffeine is
often the primary focus when the negative health effects
of coffee are discussed.
Implications of Decaffeination Methods
The decaffeination process itself is not always
innocuous. There are three common decaffeination
methods: the use of one of two organic solvents, either
methylene chloride or ethyl acetate; water extraction
known as the Swiss water process or European water
process; and supercritical carbon dioxide. Eighty percent
of decaffeinated coffee is processed with solvents. The
health effects of these solvents as found in decaffeinated
coffee are not well known, but studies suggest that
methylene chloride (dichloromethane) is shown to be
carcinogenic, and the National Cancer Institute’s list of
chemicals labels it as a possible human carcinogen. In
the decaffeination process, the solvents are removed
from the coffee beans, but residues have still been found
in decaffeinated coffee and tea. When water and carbon
dioxide are used to decaffeinate coffee, a measurable
residue is not left behind in the remaining beans, but
Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44
© 2015, IJCRCPS. All Rights Reserved 42
high acidity and other phytochemicals found in coffee
remain. Additionally, in the process of water extraction,
unique flavor characteristics of coffees from different
origins are blended and blurred water extraction due to
the intermingling of the flavors from various types of
beans in the water bath. Among the decaffeination
methods, methylene chloride extraction retains the
most flavors but leaves a dry taste in the mouth; both
water extraction and CO2 extraction blur the flavor of
the beans and ethyl acetate adds a sweet fruit flavor.
Additionally, inferior beans that may be old or moldy
are often used for decaffeination because the process
can remove off flavors and mask the age or condition
of the beans.
Biodecaffeination: A natural route of
Decaffeination
Current studies suggest that, for people who are
sensitive to coffee’s effects, decaffeinated brews may
still exacerbate their health problems Biodecaffeination
can be defined as the removal of caffeine from coffee,
tea and other caffeine containing materials by the
action of externally added microbial cells or enzymes
2
.
The concept of biodecaffeination is a relatively new
area of decaffeination and there is a growing interest
in this area of biotechnology due the advantages it
offers like being environmentally safe, economical and
in preserving the quality of the beverages
3
.
Development of biological or enzymatic methods of
decaffeination demands a deep understanding of the
caffeine metabolism in microbial systems. Detailed
information on different enzymes involved in the
degradation of caffeine in different organisms could
help in developing an enzymatic process for caffeine
removal
4
.
According to FDA guidelines, decaffeinated coffee
must have 97% of the caffeine removed. In actuality,
the caffeine content of coffee beans varies widely;
therefore the caffeine content of decaffeinated coffee
also fluctuates, and can be 10mg or more per 12
ounce cup. Other than biodecaffeination, alternative
methods fail to live up to the standards.
The present investigation is a preliminary attempt to
check the effect of the isolated strain of
Brevibacterium on different coffee samples with
reference to caffeine degradation. An HPLC analysis
of standard caffeine is checked out to compare the
effect of caffeine degradation by Brevibacterium on
different coffee samples. 10 different samples are
screened for caffeine degrading efficiency by
Brevibacterium.
Materials and Methods
Amplification of the caffeine tolerant bacteria
Solid screening medium (SSM) for amplifying the
caffeine-tolerant bacteria was prepared by mixing the
mineral solution with caffeine (2.5 g/ L) and agar
(1.5%) and autoclaved at 121°C for 10 min. Liquid
amplifying medium (LAM) was obtained after addition
of caffeine (0.5 g /L) and sucrose/glucose (5.0 g /L) in
the mineral solution and disinfection. The amplified
bacteria were used for further studies of
biodecaffeination.
Sample Analysis
The samples of Coffee of different manufacturers, teas
and colas were procured from the local market and
labelled Caffeine Samples CS3 to CS12. Samples 1 &
2 were standard caffeine procured from Himedia and
Aldrich.
The Samples were sterilized and a loopful of actively
growing culture was inoculated and incubated on a
shaker at 150rpm at a temperature of 30± 2
o
C for 96
hours. All the above processed samples were drawn
at 12 hours intervals and the growth was recorded as
an increase in the biomass by weight. Caffeine
degradation was followed by HPLC analysis of the
residual caffeine present in the medium.
Estimation of methylxanthines by high
performance liquid Chromatography (HPLC)
HPLC analysis of caffeine was performed after
incubation with Brevibacterium for 48 hours in a
Shimadzu LC 10 A- HPLC System, and the
methylxanthine compounds were separated on a C18
ODS-Luna column under isocratic conditions with 15
% acetonitrile in water at a flow rate of 1.0 ml/min.
Compounds eluting from the column were detected at
273 nm, and the peak areas were compared with
those obtained with standards of known concentration.
The percentage of caffeine degradation with residual
caffeine was obtained by the following calculation.
Area of Sample in chromatogram at RT x Standard
weight and dilution X Dilution factor X Sample 0.25 g
make up to 200mL X 100/ Area of Standard Caffeine
at RT (5.626) X 100 X 100 X 0.25.
Results and Discussion
Estimation of methylxanthines by high
performance liquid Chromatography (HPLC)
The degradation of caffeine was analyzed and found
as 82.6, 64.42, 45.84, 11.06 and 5.92 with coffee
Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44
© 2015, IJCRCPS. All Rights Reserved 43
sample (CS) 3 to 7 respectively (Table 1) and the
degradation of caffeine was analyzed and found to be
80.07, 59.77, 41.37, 20.30 with CS 8 to 12
respectively.
.Table 1 HPLC tables showing percentage of caffeine degradation
SAMPLE NAME SAMPLE
VOLUME
RETENTION
TIME
AREA PEAK
HEIGHT
%OF
CAFFEINE
REDUCED
CAFFEINE
STANDARD 1
20µl 5.626 1501220 92197 84
CAFFEINE
STANDARD 2
20 µl 5.621 1904197 141389 79
CS 3 20 µl 5.614 1566822 118725 82.6
CS 4 20 µl 5.627 1221664 92319 64.42
CS 5 20 µl 5.645 869130 66704 45.84
CS 6 20 µl 5.641 214755 16605 11.06
CS 7 20 µl 5.637 118936 8239 5.92
CS 8 20 µl 5.685 1574250 111111 80.07
CS 9 20 µl 5.645 1174769 84847 59.77
CS 10 20 µl 5.608 813148 58871 41.37
CS 11 20 µl 5.613 402884 29250 20.30
CS 12 20 µl 5.630 173009 12359 8.81
The Coffee samples responded better than teas and
colas as there might be polyphenol interactions from
the other two samples. CS 3 and 8 responded better
to biodecaffeination with almost 80% caffeine reduced.
CS 7 and CS12 were found to respond
biodecaffeination the least with 5.92 and 8.81 %
caffeine reduced.
Conclusion
The isolate Brevibacterium being reported is an
efficient caffeine degrader, which may prove useful in
the development of an environmental friendly
biodecaffeination process.
References
1. Mazzafera P, Crozier A& Magalhaes, A.C, Caffeine
metabolism in Coffee arabica and other species of
coffee. Phytochem.30(1991) 3913–16.
2. Gokulakrishnan S,K.Chandraraj & Gummadi
S.N,Microbial and enzymatic methods for the
removal of caffeine. Enzyme. Microb. Technol. 37
(2005) 225-232.
3. Dash S. S, and Gummadi S. N. Biodegradation of
caffeine by Pseudomonas sp. NCIM 5235. Res. J.
Microbiol. 1(2006)115-123.
4. Friedman J & Waller G.R., Caffeine hazards and
their prevention in germinating seeds of coffee
(Coffea arabica L.) J. Chem. Ecol. 9(1983a) 1099-
1106.
Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44
© 2015, IJCRCPS. All Rights Reserved 44
5. Kihlman B.A, Effects of caffeine on the genetic
material. Mutant Res.26 (1974)53– 71.
6. Kurtzmann R.H & Schwimmer S, Caffeine removal
from growth media by microorganisms. Experientia.
127(1973) 481-482.
7. Mazzafera P, Olsson O & Sandberg G,
Degradation of caffeine and related methyl
xanthines by Serratia marcescens isolated from
soil under coffee cultivation. Microb Ecol. 31
(1994b)199–207.
8. Mennett R.H & Nakayama T.O.M., Influence of
Temperature on Substrate and Energy Conversion
in Pseudomonas fluorescence, Appl Microbiol.22
(5)(1971)772–776.
9. Sundarraj C. V & Dhala S, Effect of Naturally
Occurring Xanthines on Bacteria I. Antimicrobial
Action and Potentiating Effect on Antibiotic
Spectra, Appl. Microbiol. 13(3)(1965)432–436.
10.Woolfolk C.A, Metabolism of N- methylpurines by a
Pseudomonas putida strain isolated by enrichment
on caffeine as the sole source of carbon and
nitrogen. J. Bacteriol, 123(1975)1088-1106.
11.Yano Y.D.M & Mazzafera P, Degradation of
caffeine by Pseudomonas putida isolated from soil.
Allel. J5(1998)23–34.

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BIO DECAFFEINATION-A STUDY ON THE EFFECTS OF BREVIBACTERIUM ON DIFFERENT SAMPLES OF COFFEE, TEA AND COLA CONTAINING CAFFEINE

  • 1. Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44 © 2015, IJCRCPS. All Rights Reserved 41 INTERNATIONAL JOURNAL OF CURRENT RESEARCH IN CHEMISTRY AND PHARMACEUTICAL SCIENCES (p-ISSN: 2348-5213: e-ISSN: 2348-5221) www.ijcrcps.com Research Article BIO DECAFFEINATION-A STUDY ON THE EFFECTS OF BREVIBACTERIUM ON DIFFERENT SAMPLES OF COFFEE, TEA AND COLA CONTAINING CAFFEINE J. SUMITHA*, C.RATHNAVEL1 AND T. SIVAKUMAR2 *Research and Development Centre, Bharathiar University, Coimbatore-641 046, Tamil Nadu, India *PG Department of Microbiology, JBAS College for Women, Teynampet, Chennai-600 018, Tamil Nadu, India 1 Department of Chemistry, Manonmaniam Sundaranar University, Abhishekapatti,Tirunelveli-627012,Tamilnadu,India 2 Department of Microbiology, Kanchi Shri Krishna College of Arts and Science, Kilambi, Kanchipuram-631551, Tamil Nadu, India *Corresponding author Abstract HPLC analysis of caffeine was performed in SHIMADZU LC 20 – AD system, and the caffeine compounds were separated on a C18 column under isocratic conditions with 40% methanol in water at a flow rate of 1.0 ml/min. Compounds eluting from the column were detected and the peak areas were compared with those obtained with standards of known concentration. The HPLC analysis of caffeine degradation by Brevibacterium is done by injecting the sample volume of about 20µl HPLC analysis is done for the sample at different incubation periods with standard caffeine concentration (Known). The sample is analyzed for every twelve hours of incubation and peak values are obtained. Caffeine concentration is an important parameter to be checked as excessive consumption of caffeine leads to many health hazards. Keywords: , Biodecaffeination, Brevibacterium, HPLC. Introduction Caffeine Caffeine is found in about a hundred species of plants, but the most highly cultivated sources are the coffee beans, (Coffea arabica or Coffea canephora, variety robusta), the leaves & leaf-buds of tea (Thea sinensis or Camellia sinensis), cola nuts (Cola acuminata) and cocoa beans (Theobroma cacao).Coffee and tea plants are the major sources of natural caffeine and related compounds such as theophylline and theobromine 1 . A very large proportion of the non-alcoholic beverages used in social settings contain caffeine. The most important beverages and foods containing caffeine are coffee, tea, cola nuts, cola drinks, cocoa, and chocolate. The present study employs different coffee samples to test the bio-decaffeinating effect. Caffeine is often the primary focus when the negative health effects of coffee are discussed. Implications of Decaffeination Methods The decaffeination process itself is not always innocuous. There are three common decaffeination methods: the use of one of two organic solvents, either methylene chloride or ethyl acetate; water extraction known as the Swiss water process or European water process; and supercritical carbon dioxide. Eighty percent of decaffeinated coffee is processed with solvents. The health effects of these solvents as found in decaffeinated coffee are not well known, but studies suggest that methylene chloride (dichloromethane) is shown to be carcinogenic, and the National Cancer Institute’s list of chemicals labels it as a possible human carcinogen. In the decaffeination process, the solvents are removed from the coffee beans, but residues have still been found in decaffeinated coffee and tea. When water and carbon dioxide are used to decaffeinate coffee, a measurable residue is not left behind in the remaining beans, but
  • 2. Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44 © 2015, IJCRCPS. All Rights Reserved 42 high acidity and other phytochemicals found in coffee remain. Additionally, in the process of water extraction, unique flavor characteristics of coffees from different origins are blended and blurred water extraction due to the intermingling of the flavors from various types of beans in the water bath. Among the decaffeination methods, methylene chloride extraction retains the most flavors but leaves a dry taste in the mouth; both water extraction and CO2 extraction blur the flavor of the beans and ethyl acetate adds a sweet fruit flavor. Additionally, inferior beans that may be old or moldy are often used for decaffeination because the process can remove off flavors and mask the age or condition of the beans. Biodecaffeination: A natural route of Decaffeination Current studies suggest that, for people who are sensitive to coffee’s effects, decaffeinated brews may still exacerbate their health problems Biodecaffeination can be defined as the removal of caffeine from coffee, tea and other caffeine containing materials by the action of externally added microbial cells or enzymes 2 . The concept of biodecaffeination is a relatively new area of decaffeination and there is a growing interest in this area of biotechnology due the advantages it offers like being environmentally safe, economical and in preserving the quality of the beverages 3 . Development of biological or enzymatic methods of decaffeination demands a deep understanding of the caffeine metabolism in microbial systems. Detailed information on different enzymes involved in the degradation of caffeine in different organisms could help in developing an enzymatic process for caffeine removal 4 . According to FDA guidelines, decaffeinated coffee must have 97% of the caffeine removed. In actuality, the caffeine content of coffee beans varies widely; therefore the caffeine content of decaffeinated coffee also fluctuates, and can be 10mg or more per 12 ounce cup. Other than biodecaffeination, alternative methods fail to live up to the standards. The present investigation is a preliminary attempt to check the effect of the isolated strain of Brevibacterium on different coffee samples with reference to caffeine degradation. An HPLC analysis of standard caffeine is checked out to compare the effect of caffeine degradation by Brevibacterium on different coffee samples. 10 different samples are screened for caffeine degrading efficiency by Brevibacterium. Materials and Methods Amplification of the caffeine tolerant bacteria Solid screening medium (SSM) for amplifying the caffeine-tolerant bacteria was prepared by mixing the mineral solution with caffeine (2.5 g/ L) and agar (1.5%) and autoclaved at 121°C for 10 min. Liquid amplifying medium (LAM) was obtained after addition of caffeine (0.5 g /L) and sucrose/glucose (5.0 g /L) in the mineral solution and disinfection. The amplified bacteria were used for further studies of biodecaffeination. Sample Analysis The samples of Coffee of different manufacturers, teas and colas were procured from the local market and labelled Caffeine Samples CS3 to CS12. Samples 1 & 2 were standard caffeine procured from Himedia and Aldrich. The Samples were sterilized and a loopful of actively growing culture was inoculated and incubated on a shaker at 150rpm at a temperature of 30± 2 o C for 96 hours. All the above processed samples were drawn at 12 hours intervals and the growth was recorded as an increase in the biomass by weight. Caffeine degradation was followed by HPLC analysis of the residual caffeine present in the medium. Estimation of methylxanthines by high performance liquid Chromatography (HPLC) HPLC analysis of caffeine was performed after incubation with Brevibacterium for 48 hours in a Shimadzu LC 10 A- HPLC System, and the methylxanthine compounds were separated on a C18 ODS-Luna column under isocratic conditions with 15 % acetonitrile in water at a flow rate of 1.0 ml/min. Compounds eluting from the column were detected at 273 nm, and the peak areas were compared with those obtained with standards of known concentration. The percentage of caffeine degradation with residual caffeine was obtained by the following calculation. Area of Sample in chromatogram at RT x Standard weight and dilution X Dilution factor X Sample 0.25 g make up to 200mL X 100/ Area of Standard Caffeine at RT (5.626) X 100 X 100 X 0.25. Results and Discussion Estimation of methylxanthines by high performance liquid Chromatography (HPLC) The degradation of caffeine was analyzed and found as 82.6, 64.42, 45.84, 11.06 and 5.92 with coffee
  • 3. Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44 © 2015, IJCRCPS. All Rights Reserved 43 sample (CS) 3 to 7 respectively (Table 1) and the degradation of caffeine was analyzed and found to be 80.07, 59.77, 41.37, 20.30 with CS 8 to 12 respectively. .Table 1 HPLC tables showing percentage of caffeine degradation SAMPLE NAME SAMPLE VOLUME RETENTION TIME AREA PEAK HEIGHT %OF CAFFEINE REDUCED CAFFEINE STANDARD 1 20µl 5.626 1501220 92197 84 CAFFEINE STANDARD 2 20 µl 5.621 1904197 141389 79 CS 3 20 µl 5.614 1566822 118725 82.6 CS 4 20 µl 5.627 1221664 92319 64.42 CS 5 20 µl 5.645 869130 66704 45.84 CS 6 20 µl 5.641 214755 16605 11.06 CS 7 20 µl 5.637 118936 8239 5.92 CS 8 20 µl 5.685 1574250 111111 80.07 CS 9 20 µl 5.645 1174769 84847 59.77 CS 10 20 µl 5.608 813148 58871 41.37 CS 11 20 µl 5.613 402884 29250 20.30 CS 12 20 µl 5.630 173009 12359 8.81 The Coffee samples responded better than teas and colas as there might be polyphenol interactions from the other two samples. CS 3 and 8 responded better to biodecaffeination with almost 80% caffeine reduced. CS 7 and CS12 were found to respond biodecaffeination the least with 5.92 and 8.81 % caffeine reduced. Conclusion The isolate Brevibacterium being reported is an efficient caffeine degrader, which may prove useful in the development of an environmental friendly biodecaffeination process. References 1. Mazzafera P, Crozier A& Magalhaes, A.C, Caffeine metabolism in Coffee arabica and other species of coffee. Phytochem.30(1991) 3913–16. 2. Gokulakrishnan S,K.Chandraraj & Gummadi S.N,Microbial and enzymatic methods for the removal of caffeine. Enzyme. Microb. Technol. 37 (2005) 225-232. 3. Dash S. S, and Gummadi S. N. Biodegradation of caffeine by Pseudomonas sp. NCIM 5235. Res. J. Microbiol. 1(2006)115-123. 4. Friedman J & Waller G.R., Caffeine hazards and their prevention in germinating seeds of coffee (Coffea arabica L.) J. Chem. Ecol. 9(1983a) 1099- 1106.
  • 4. Int. J. Curr.Res.Chem.Pharma.Sci. 2(8): (2015):41–44 © 2015, IJCRCPS. All Rights Reserved 44 5. Kihlman B.A, Effects of caffeine on the genetic material. Mutant Res.26 (1974)53– 71. 6. Kurtzmann R.H & Schwimmer S, Caffeine removal from growth media by microorganisms. Experientia. 127(1973) 481-482. 7. Mazzafera P, Olsson O & Sandberg G, Degradation of caffeine and related methyl xanthines by Serratia marcescens isolated from soil under coffee cultivation. Microb Ecol. 31 (1994b)199–207. 8. Mennett R.H & Nakayama T.O.M., Influence of Temperature on Substrate and Energy Conversion in Pseudomonas fluorescence, Appl Microbiol.22 (5)(1971)772–776. 9. Sundarraj C. V & Dhala S, Effect of Naturally Occurring Xanthines on Bacteria I. Antimicrobial Action and Potentiating Effect on Antibiotic Spectra, Appl. Microbiol. 13(3)(1965)432–436. 10.Woolfolk C.A, Metabolism of N- methylpurines by a Pseudomonas putida strain isolated by enrichment on caffeine as the sole source of carbon and nitrogen. J. Bacteriol, 123(1975)1088-1106. 11.Yano Y.D.M & Mazzafera P, Degradation of caffeine by Pseudomonas putida isolated from soil. Allel. J5(1998)23–34.