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@ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1029
ISSN No: 2456 - 6470 | www.ijtsrd.com | Volume - 1 | Issue – 5
International Journal of Trend in Scientific
Research and Development (IJTSRD)
International Open Access Journal
Microbial Decolorization of Leather Dye Effluent
Dr. Jitender Kumar
Head, Department of Biotechnology,
Hans Raj Mahila Mahavidyalaya, Jalandhar
Navleen Kaur Chopra
Research Scholar (Ph.D.), I.K. Gujral Punjab
Technical University, Kapurthala
ABSTRACT
As we know 71% of Earth's Surface is covered with
water. Water is one of the most essential element for
the persistence of life on this planet. Pure and
contamination free water is the dire necessity of every
living being present on Earth but today water
pollution has posed great threat to the existence of
life. The discharge of effluents from various industries
into the water bodies are mainly responsible for water
pollution specially effluents from leather industry are
the most contaminating as along with the harmful
chemicals they contain organic matter as well. The
dyes disposed by the leather industry are the most
harmful for the environment. The conventional
physicochemical methods used for the treatment of
leather dyes in the contaminated water i.e.
coagulation, precipitation, oxidation etc have
disadvantages and limitations. This study presents
microbial decolorization of leather dye effluents from
Shigella sp. isolated from effluent samples collected
from leather industry. Different parameters such as
temperature and pH were optimized for decolorization
of Methylene Blue, Crystal Violet, EosinYellow,
Safranine dyes by using bacterial isolates. Optimum
temperature for decolorization was observed to be
300
c, the optimum pH range for decolorization was
found to be from pH6-pH8. All the samples were
incubated at 30°C 150 rpm. The decolorization was
measured as decrease in absorbance maxima at 663
nm, 590 nm, 518nm, 530 nm for mehtylene blue,
crystal violet, eosin yellow, safranine respectively.
Keywords: shigella sp. Crystal Violet, Methylene
Blue.Eosin Yellow, Safranine
INTRODUCTION
Potable water is one of the primary necessities for the
existence of life on this earth. Water is essential for
daily human activities may it be for domestic
purposes, industrial or agricultural purposes. With the
increase in urbanization and industrialization the
environment has been remarkably affected by man.
With the increase in population we have witnessed a
rapid increase in pollution mainly water pollution.
The discharge of effluents from industries into the
water bodies has emerged out to be the main culprit of
water pollution. Indian tannery industry is one of the
leading tannery industries in the world but with that it
also one of highly polluting industry. Tannery
effluents lead to both water as well as air pollution.
On the basis of volume of tannery effluents and its
composition it has been regarded as most polluting
among all [2], [4], [13], [15]. The studies have
reported that waste water discharged from tannery
industry have greater values of BOD, COD, color and
pH [14], [17].
The colored components of tannery effluent along
with organic load causes ecological imbalance in the
receiving water body [9]. Tannery waste water
discharges large amount of dye during washing
operations [8]. These dyes are mainly xenobiotic and
also carcinogenic in some cases [3]. Studies have also
reported allergic effect of these dyes [11], [12]. If not
International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470
@ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1030
treated properly these dyes persist in the environment for a long duration of time.
Use of synthetic dye is more prevalent than natural
dyes as they are cost effective their production is easy,
large variety of shades can be produced moreover due
to comparative fastness of colour than natural dyes.
More than 100,000 dyes are commercially available
and about one million ton of these dyes are produced
annually worldwide [1]. During industrial process,
approximately 10-15% of these dyes are released into
the environment [6] due to their chemical nature these
dyes pose great threat to environment.
Addition of colour to water is the main indication of
the water pollution. Highly coloured synthetic dyes
block the entry of sunlight in the receiving water
body, hence are fatal for flora and fauna living in it.
Moreover dyes and their breakdown product are
cytotoxic and carcinogenic [7]. A number of
physiochemical methods such as coagulation,
filtration, precipitation, oxidation etc. have been used
to treat effluent containing synthetic dyes, but these
methods have many disadvantages and limitations. It
is therefore important to develop efficient and cost
effective methods for decolorization and degradation
of dyes in tannery effluents.
In situ degradation of dyes by microorganisms is a
novel method for treatment of effluent. In this
method, the microorganisms isolated from the site of
pollution can be used for the treatment of effluent [9].
The present study aims to isolate dye decolorzing
microorganisms from the tannery effluents. As the
microbial isolates will be isolated from the tannery
wastewater, they can easily adopt the prevailing
environment. Such microorganisms can be used to
develop effective biological treatment system for
waste water contaminated with leather dyes. Further
present research aims to study the decolorization
capacity of such microorganisms by screening them
from effluent, isolation and optimization of
decolorization conditions (temperature, pH etc.),
hence to produce a system to treat leather dyes in an
ecofriendly manner with the help of microbes.
MATERIALS AND METHODS:
➢ Chemicals and Media
Dye effluents were collected from a Leather Complex
Jalandhar Punjab. All microbiological media and
medium ingredients were purchased from HiMedia
Laboratories (Mumbai, MH, India).
➢ Isolation dye degrading Bacteria
The Leather Dye containing effluent sample was
collected from a Leather industry located at Jalandhar,
Punjab. One ml of effluent was transferred into 9 ml
of distilled water in sterile test tubes. Serial dilution
was done up to 10 by thorough mixing. 0.1 ml of
sample from each dilution was spread on Nutrient
Agar plates containing with the help of sterile L-rod.
The petridishes were incubated at 300
C for 24 hours
from these bacterial colonies were isolated by Streak
Plate Method.
➢ Preservation and maintenance
Pure bacterial isolates were obtained on the Nutrient
agar plates were stored in refrigerator and served as
stock cultures. Subcultures were routinely made every
7 to 10 days.
➢ Screening of decolorizing Bacteria
All the isolates were selected for screening of
decolorizing activity of dye. Inoculums each isolate
were added to 100 ml of Nutrient Broth and were
incubated at 30 0
C for 48 hours.1% of dye solution
was serially diluted from 10-1
to 10-
5. These solutions
were inoculated with 1% of nutrient broth and
incubated at 30 0
C for 6 days. After 6 days, effective
decolorization was seen visually. Those isolates
showing decolorization of textile dye effluent were
selected for further studies with decolorization of
synthetic dyes methylene blue, crystal violet, eosin
yellow, safranine. The bacterial strain found to be
potential in dye decolorization was selected and best
decolorization results were observed in 10-4
dilution.
➢ Biochemical characterization
Furthermore the microbial isolate selected on the
basis of optimum decolourization activity was
characterized biochemically as well as physiologically
up to species level.
➢ Decolorization assay
Decolorization activity in terms of percent
decolorization was determined by following method
described by (Ponraj et.al). 10 ml of sample was
centrifuged at 1000 rpm for 10 minutes.
Spectrophotometer was used for absorbance
measurement. The decrease in absorbance was
monitored at 663 nm, 590 nm, 518nm, 530 nm for
Methylene Blue, Crystal Violet, Eosin Yellow and
Safranine respectively. Decolorization activity was
International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470
@ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1031
calculated according to the following formula: D= [A
-F )/A ] x 100
Where: D, decolourization; A initial absorbance; F
final absorbance (ponraj et .al)[10].
➢ Dye Decolorization Optimization
Decolorization of methylene blue, crystal violet, eosin
yellow, safranine by selected bacterial isolate was
optimized with respect to the effect temperature (40
C,
270
C, 370C
, 600
C) and pH(2,4,6,8,10).Dye solution
without culture served as control. All the test tubes
were incubated at 30 0
C under shaking conditions 100
rpm for 6 days.
RESULTS AND DISCUSSION
The complication faced during treatment of water
pollution is the degradation of synthetic dyes disposed
in the water bodies through industrial effluents.
Tannery effluents being most polluting need to be
paid most attention. Indian tanning industry is one of
the leading tanning industries in the world. The
tanning of leather involves use of many toxic
chemicals to process and dye the leather. These
chemicals cause life threatening problems like cancer,
damage to lungs and kidneys etc. to the living being
coming in contact with them. So there is an urgent
requirement for the treatment of the water polluted by
the effluents from various industries specially the dye
containing effluent from the leather industry. The
method devised has to be eco-friendly and cost
effective so as to make it viable on large scale. In the
present study microbial decolourization of leather dye
effluent was carried out using the bacterial isolate
obtained from the leather dye effluent. Leather dye
effluent samples were collected from the disposal site
of effluent for screening efficient microorganisms,
(bacteria).
➢ Screening of dye decolorization Bacteria
The obtained bacterial isolates showed decolorization
of dyes after 6 days of incubation at 30°C under
shaking (100 rpm). In the present investigation the
rate of color removed increased with incubation
periods.
➢ Bacterial isolated by streak plate method
Decolorization of Crystal Violet dye after 6 days
incubation
Biochemical Characterization
Biochemical characterization of the bacterial isolate
revealed the following results:-
TEST RESULT
H2S (TSI)
Urease
Indole
Methyl red (37 0
C)
Voges–Proskauer(37 0
C)
Simmons’ citrate
Christensen’s citrate
Sodium acetate
Mucate
KCN
Motility
Sodium malonate
Lysine decarboxylase
Arginine dihydrolase
Ornithine decarboxylase
Phenylalanine deaminase
Galactosidase (ONPG)
Catalase
Oxidase
Glucose (acid)
Glucose (gas)
Lactose
Sucrose
Mannitol
Salicin
Adonitol
Dulcitol
Inositol
Arabinose
Sorbitol
Raffinose
Rhamnose
Maltose
Xylose
Trehalose
-
-
Variable
+
-
-
-
-
-
-
-
-
-
-
-
-
-
+
-
+
-
-
-
+
-
-
-
-
+
+
-
-
-
+
+
International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470
@ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1032
Cellobiose
Mannose
Glycerol
Esculin
-
+
+
-
The potential strain was identified as Shigella sp.
➢ Optimization of dye Decolorization
For the maximization of decolourization of the dyes
Methylene Blue, Crystal Violet, Eosin Yellow,
Safranine by the selected bacterial isolates,
experiments were conducted for optimization of
temperature and Ph.
➢ Effect of Temperatures
Different temperatures used were as refrigerator
temperature (4°C), room temperature (27°C),
incubator temperature (37°C) and extreme
temperatures (60 °C). The maximum decolorization
was observed 27 C followed by 37 C and 4 C, least
decolorizaton was observed at 60°C as cells does not
remain viable at high temperatures(Figure- 1). Similar
results were obtained by Ponraj et.al [10] who used by
different bacterial strains for studying decolorization.
Temperature
% Decolorization
Methylene
Blue
Crystal
Violet
Eosin
yellow
Saffranine
4°C 5.5 3.2 4.7 6.1
27°C 64.3 65.7 61.2 50.4
37°C 50.8 54.6 53.4 42.6
60°C 28.4 29.6 31.7 17.8
Figure -1 Effect of temperature on decolorzation of
dyes by Shigella Sp.
➢ Effect of pH
The five bacterial isolates were grown in medium
with different pH (2,4,6,8,10). The pH of the medium
was adjusted with HCl and NaOH. The maximum
percentage decolorization was observed between pH 6
to 8. (Figure-2) Similar results were seen in studies
carried by Wong et.al and Hu et.al [16], [5].
pH % Decolorization
Methylen
e
Blue
Crystal
Violet
Eosin
yellow
Saffranin
e
2 2.6 3.5 4.9 6.9
4 24.8 25.5 21.6 23.6
6 50.8 54.6 53.4 42.5
8 58.4 59.4 55.7 58.7
10 16.7 17.6 18.7 19
0
10
20
30
40
50
60
70
%Decolorization
Dyes
4°C
27°C
37°C
60°C
International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470
@ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1033
Figure -2 Effect of pH on decolorzation dyes by
Shigella Sp.
CONCLUSION
The present study reveals that all the four dyes
methylene blue, crystal violet, eosin yellow, safranine
are degradable under aerobic conditions with Shigela
isolated from textile dye effluent.The bacteria
exhibhited maximum decolorization ability between
pH6-pH8 Whereas temperature did not showed
considerable effect on on decolorization 27°C-37°C
showed best decolorization results based on these
results we can carry out further studies and device a
eco friendly cost effective and efficient system for the
degradation of leather dyes in the industrial effluents.
REFERENCES
[1] Adedayo O, Javadpour S, Taylor C, Anderson
WA, Moo-Young M (2004) Decolourization and
detoxification of methyl red by aerobic bacteria
from a wastewater treatment plant. World J
Microbiol Biotech, 20: 545– 550.
[2] Awomeso JA, Taiwo AM, Gbadebo AM,
Adenowo JA (2010). Studies on the pollution of
waterbody by tannery industry effluents in
Lagos, Nigeria. J Appl Sci Environ Sanit, 5:353-
359.
[3] Daneshvar N, Ayazloo M, Khatae AR, Pourhassan
M (2007) Biological decolorization of dye
solution containing malachite black by microalgae
Cosmarium sp . Biores Technol, 98:1176- 1182.
[4] Gurulakshmi M, Sudarmani DNP, Venba R
(2008) Biodegradation of leather acid dye by
Bacillus subtilis. Advanced Biotech, 47: 2-8.
[5] Hu TL (1994) Decolourization of reactive azo
dyes by transformation with Pseudomonas luteola.
Biores Tech, 49: 47–51.
[6] Keharia H, Patel H, Madamwar D (2004)
Decolorization screening of synthetic dyes by
anaerobic methanogenic sludge using a Bacth-
decoloration assay. World J Microbiol Biotechnol,
20: 365-370.
[7] Khehra MS, Saini HS, Sharma DK, Chadha BS,
Chimni SS (2006). Biodegradation of azo dye C.I.
Acid Red 88 by an anoxic-aerobic sequential
bioreactor. Dyes and Pigments, 70:1-7
[8] Mathur N, Bhatnagar P, Bakre P (2006) Assessing
mutagenicity of tannery dyes from Pali
(Rajasthan) using Ames bioassay. Appl Ecol
Environ Res, 4(1):111 - 118.
[9] Puvaneswari N, Muthukrishnan J, Gunasekaran
P (2006) Toxicity assessment and microbial
degradation of azodyes. Ind J Exp Biol, 44:618-
626.
[10] Ponraj.M,Gokila.K,and Zambare
Vasudeo(2011).Bacterial decolorization of textile
Dye –Orange 3R.International Journal of
advanced Biotechnology and Research.,2(1)168-
177
[11] Sasaki K, Sakai M, Matusita K, Masuda Y,
Sato K (2008) Chemical structure analysis for azo
type disperse dyes by mass spectroscopy and
detection of dyestuff in tannery products causing
allergic contact dermatitis. The Jap Soc Analyt
Chem: Bunseki Kagaku, 57: 833-850.
[12] Saunders H, O Brien T, Nixon R (2004)
Tannery dye allergic contact dermatitis following
paraphenylenediamine sensitization from a
temporary tattoo. Aus J Dermatol, 45(4):229 -
231.
[13] Shitole VH, Panvalkar SS (2000)
Bioremediation of tannery effluent. J Emp Bio,
1(2):10..
[14] Tufekci N, Sivri N, Toroz I (2007) Pollutants
of tannery industry wastewater and assessment of
its discharge limits by water quality standards.
Turk J Fish Aquat Sci, 7(2): 97- 103.
[15] Vilaseca M, Gutie MC, Grimau VL, Mesas
ML, Crespi M (2010) Biological treatment of a
tannery effluent after electrochemical oxidation of
reactive dyes. Water Environ Res, 82(2):176-182.
DOI:
[16] Wong PK, Yuen, PY (1996) Decolourization
of synthetic dyes by Klebsiella pneumoniae RS-
13. Water Res, 30: 1736-1744.
[17] Yusuff RO, Sonibare JA (2004)
Characterization of tannery industries effluents in
Kaduna, Nigeria and pollution implications.
Global Nest: The Int J, 6(3): 212 -221.
0
10
20
30
40
50
60
70
%Decolorization
Dyes
2
4
6
8
10

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Microbial Decolorization of Leather Dye Effluent

  • 1. @ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1029 ISSN No: 2456 - 6470 | www.ijtsrd.com | Volume - 1 | Issue – 5 International Journal of Trend in Scientific Research and Development (IJTSRD) International Open Access Journal Microbial Decolorization of Leather Dye Effluent Dr. Jitender Kumar Head, Department of Biotechnology, Hans Raj Mahila Mahavidyalaya, Jalandhar Navleen Kaur Chopra Research Scholar (Ph.D.), I.K. Gujral Punjab Technical University, Kapurthala ABSTRACT As we know 71% of Earth's Surface is covered with water. Water is one of the most essential element for the persistence of life on this planet. Pure and contamination free water is the dire necessity of every living being present on Earth but today water pollution has posed great threat to the existence of life. The discharge of effluents from various industries into the water bodies are mainly responsible for water pollution specially effluents from leather industry are the most contaminating as along with the harmful chemicals they contain organic matter as well. The dyes disposed by the leather industry are the most harmful for the environment. The conventional physicochemical methods used for the treatment of leather dyes in the contaminated water i.e. coagulation, precipitation, oxidation etc have disadvantages and limitations. This study presents microbial decolorization of leather dye effluents from Shigella sp. isolated from effluent samples collected from leather industry. Different parameters such as temperature and pH were optimized for decolorization of Methylene Blue, Crystal Violet, EosinYellow, Safranine dyes by using bacterial isolates. Optimum temperature for decolorization was observed to be 300 c, the optimum pH range for decolorization was found to be from pH6-pH8. All the samples were incubated at 30°C 150 rpm. The decolorization was measured as decrease in absorbance maxima at 663 nm, 590 nm, 518nm, 530 nm for mehtylene blue, crystal violet, eosin yellow, safranine respectively. Keywords: shigella sp. Crystal Violet, Methylene Blue.Eosin Yellow, Safranine INTRODUCTION Potable water is one of the primary necessities for the existence of life on this earth. Water is essential for daily human activities may it be for domestic purposes, industrial or agricultural purposes. With the increase in urbanization and industrialization the environment has been remarkably affected by man. With the increase in population we have witnessed a rapid increase in pollution mainly water pollution. The discharge of effluents from industries into the water bodies has emerged out to be the main culprit of water pollution. Indian tannery industry is one of the leading tannery industries in the world but with that it also one of highly polluting industry. Tannery effluents lead to both water as well as air pollution. On the basis of volume of tannery effluents and its composition it has been regarded as most polluting among all [2], [4], [13], [15]. The studies have reported that waste water discharged from tannery industry have greater values of BOD, COD, color and pH [14], [17]. The colored components of tannery effluent along with organic load causes ecological imbalance in the receiving water body [9]. Tannery waste water discharges large amount of dye during washing operations [8]. These dyes are mainly xenobiotic and also carcinogenic in some cases [3]. Studies have also reported allergic effect of these dyes [11], [12]. If not
  • 2. International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470 @ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1030 treated properly these dyes persist in the environment for a long duration of time. Use of synthetic dye is more prevalent than natural dyes as they are cost effective their production is easy, large variety of shades can be produced moreover due to comparative fastness of colour than natural dyes. More than 100,000 dyes are commercially available and about one million ton of these dyes are produced annually worldwide [1]. During industrial process, approximately 10-15% of these dyes are released into the environment [6] due to their chemical nature these dyes pose great threat to environment. Addition of colour to water is the main indication of the water pollution. Highly coloured synthetic dyes block the entry of sunlight in the receiving water body, hence are fatal for flora and fauna living in it. Moreover dyes and their breakdown product are cytotoxic and carcinogenic [7]. A number of physiochemical methods such as coagulation, filtration, precipitation, oxidation etc. have been used to treat effluent containing synthetic dyes, but these methods have many disadvantages and limitations. It is therefore important to develop efficient and cost effective methods for decolorization and degradation of dyes in tannery effluents. In situ degradation of dyes by microorganisms is a novel method for treatment of effluent. In this method, the microorganisms isolated from the site of pollution can be used for the treatment of effluent [9]. The present study aims to isolate dye decolorzing microorganisms from the tannery effluents. As the microbial isolates will be isolated from the tannery wastewater, they can easily adopt the prevailing environment. Such microorganisms can be used to develop effective biological treatment system for waste water contaminated with leather dyes. Further present research aims to study the decolorization capacity of such microorganisms by screening them from effluent, isolation and optimization of decolorization conditions (temperature, pH etc.), hence to produce a system to treat leather dyes in an ecofriendly manner with the help of microbes. MATERIALS AND METHODS: ➢ Chemicals and Media Dye effluents were collected from a Leather Complex Jalandhar Punjab. All microbiological media and medium ingredients were purchased from HiMedia Laboratories (Mumbai, MH, India). ➢ Isolation dye degrading Bacteria The Leather Dye containing effluent sample was collected from a Leather industry located at Jalandhar, Punjab. One ml of effluent was transferred into 9 ml of distilled water in sterile test tubes. Serial dilution was done up to 10 by thorough mixing. 0.1 ml of sample from each dilution was spread on Nutrient Agar plates containing with the help of sterile L-rod. The petridishes were incubated at 300 C for 24 hours from these bacterial colonies were isolated by Streak Plate Method. ➢ Preservation and maintenance Pure bacterial isolates were obtained on the Nutrient agar plates were stored in refrigerator and served as stock cultures. Subcultures were routinely made every 7 to 10 days. ➢ Screening of decolorizing Bacteria All the isolates were selected for screening of decolorizing activity of dye. Inoculums each isolate were added to 100 ml of Nutrient Broth and were incubated at 30 0 C for 48 hours.1% of dye solution was serially diluted from 10-1 to 10- 5. These solutions were inoculated with 1% of nutrient broth and incubated at 30 0 C for 6 days. After 6 days, effective decolorization was seen visually. Those isolates showing decolorization of textile dye effluent were selected for further studies with decolorization of synthetic dyes methylene blue, crystal violet, eosin yellow, safranine. The bacterial strain found to be potential in dye decolorization was selected and best decolorization results were observed in 10-4 dilution. ➢ Biochemical characterization Furthermore the microbial isolate selected on the basis of optimum decolourization activity was characterized biochemically as well as physiologically up to species level. ➢ Decolorization assay Decolorization activity in terms of percent decolorization was determined by following method described by (Ponraj et.al). 10 ml of sample was centrifuged at 1000 rpm for 10 minutes. Spectrophotometer was used for absorbance measurement. The decrease in absorbance was monitored at 663 nm, 590 nm, 518nm, 530 nm for Methylene Blue, Crystal Violet, Eosin Yellow and Safranine respectively. Decolorization activity was
  • 3. International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470 @ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1031 calculated according to the following formula: D= [A -F )/A ] x 100 Where: D, decolourization; A initial absorbance; F final absorbance (ponraj et .al)[10]. ➢ Dye Decolorization Optimization Decolorization of methylene blue, crystal violet, eosin yellow, safranine by selected bacterial isolate was optimized with respect to the effect temperature (40 C, 270 C, 370C , 600 C) and pH(2,4,6,8,10).Dye solution without culture served as control. All the test tubes were incubated at 30 0 C under shaking conditions 100 rpm for 6 days. RESULTS AND DISCUSSION The complication faced during treatment of water pollution is the degradation of synthetic dyes disposed in the water bodies through industrial effluents. Tannery effluents being most polluting need to be paid most attention. Indian tanning industry is one of the leading tanning industries in the world. The tanning of leather involves use of many toxic chemicals to process and dye the leather. These chemicals cause life threatening problems like cancer, damage to lungs and kidneys etc. to the living being coming in contact with them. So there is an urgent requirement for the treatment of the water polluted by the effluents from various industries specially the dye containing effluent from the leather industry. The method devised has to be eco-friendly and cost effective so as to make it viable on large scale. In the present study microbial decolourization of leather dye effluent was carried out using the bacterial isolate obtained from the leather dye effluent. Leather dye effluent samples were collected from the disposal site of effluent for screening efficient microorganisms, (bacteria). ➢ Screening of dye decolorization Bacteria The obtained bacterial isolates showed decolorization of dyes after 6 days of incubation at 30°C under shaking (100 rpm). In the present investigation the rate of color removed increased with incubation periods. ➢ Bacterial isolated by streak plate method Decolorization of Crystal Violet dye after 6 days incubation Biochemical Characterization Biochemical characterization of the bacterial isolate revealed the following results:- TEST RESULT H2S (TSI) Urease Indole Methyl red (37 0 C) Voges–Proskauer(37 0 C) Simmons’ citrate Christensen’s citrate Sodium acetate Mucate KCN Motility Sodium malonate Lysine decarboxylase Arginine dihydrolase Ornithine decarboxylase Phenylalanine deaminase Galactosidase (ONPG) Catalase Oxidase Glucose (acid) Glucose (gas) Lactose Sucrose Mannitol Salicin Adonitol Dulcitol Inositol Arabinose Sorbitol Raffinose Rhamnose Maltose Xylose Trehalose - - Variable + - - - - - - - - - - - - - + - + - - - + - - - - + + - - - + +
  • 4. International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470 @ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1032 Cellobiose Mannose Glycerol Esculin - + + - The potential strain was identified as Shigella sp. ➢ Optimization of dye Decolorization For the maximization of decolourization of the dyes Methylene Blue, Crystal Violet, Eosin Yellow, Safranine by the selected bacterial isolates, experiments were conducted for optimization of temperature and Ph. ➢ Effect of Temperatures Different temperatures used were as refrigerator temperature (4°C), room temperature (27°C), incubator temperature (37°C) and extreme temperatures (60 °C). The maximum decolorization was observed 27 C followed by 37 C and 4 C, least decolorizaton was observed at 60°C as cells does not remain viable at high temperatures(Figure- 1). Similar results were obtained by Ponraj et.al [10] who used by different bacterial strains for studying decolorization. Temperature % Decolorization Methylene Blue Crystal Violet Eosin yellow Saffranine 4°C 5.5 3.2 4.7 6.1 27°C 64.3 65.7 61.2 50.4 37°C 50.8 54.6 53.4 42.6 60°C 28.4 29.6 31.7 17.8 Figure -1 Effect of temperature on decolorzation of dyes by Shigella Sp. ➢ Effect of pH The five bacterial isolates were grown in medium with different pH (2,4,6,8,10). The pH of the medium was adjusted with HCl and NaOH. The maximum percentage decolorization was observed between pH 6 to 8. (Figure-2) Similar results were seen in studies carried by Wong et.al and Hu et.al [16], [5]. pH % Decolorization Methylen e Blue Crystal Violet Eosin yellow Saffranin e 2 2.6 3.5 4.9 6.9 4 24.8 25.5 21.6 23.6 6 50.8 54.6 53.4 42.5 8 58.4 59.4 55.7 58.7 10 16.7 17.6 18.7 19 0 10 20 30 40 50 60 70 %Decolorization Dyes 4°C 27°C 37°C 60°C
  • 5. International Journal of Trend in Scientific Research and Development (IJTSRD) ISSN: 2456-6470 @ IJTSRD | Available Online @ www.ijtsrd.com | Volume – 1 | Issue – 5 | July-Aug 2017 Page: 1033 Figure -2 Effect of pH on decolorzation dyes by Shigella Sp. CONCLUSION The present study reveals that all the four dyes methylene blue, crystal violet, eosin yellow, safranine are degradable under aerobic conditions with Shigela isolated from textile dye effluent.The bacteria exhibhited maximum decolorization ability between pH6-pH8 Whereas temperature did not showed considerable effect on on decolorization 27°C-37°C showed best decolorization results based on these results we can carry out further studies and device a eco friendly cost effective and efficient system for the degradation of leather dyes in the industrial effluents. REFERENCES [1] Adedayo O, Javadpour S, Taylor C, Anderson WA, Moo-Young M (2004) Decolourization and detoxification of methyl red by aerobic bacteria from a wastewater treatment plant. World J Microbiol Biotech, 20: 545– 550. [2] Awomeso JA, Taiwo AM, Gbadebo AM, Adenowo JA (2010). Studies on the pollution of waterbody by tannery industry effluents in Lagos, Nigeria. J Appl Sci Environ Sanit, 5:353- 359. [3] Daneshvar N, Ayazloo M, Khatae AR, Pourhassan M (2007) Biological decolorization of dye solution containing malachite black by microalgae Cosmarium sp . Biores Technol, 98:1176- 1182. [4] Gurulakshmi M, Sudarmani DNP, Venba R (2008) Biodegradation of leather acid dye by Bacillus subtilis. Advanced Biotech, 47: 2-8. [5] Hu TL (1994) Decolourization of reactive azo dyes by transformation with Pseudomonas luteola. Biores Tech, 49: 47–51. [6] Keharia H, Patel H, Madamwar D (2004) Decolorization screening of synthetic dyes by anaerobic methanogenic sludge using a Bacth- decoloration assay. World J Microbiol Biotechnol, 20: 365-370. [7] Khehra MS, Saini HS, Sharma DK, Chadha BS, Chimni SS (2006). Biodegradation of azo dye C.I. Acid Red 88 by an anoxic-aerobic sequential bioreactor. Dyes and Pigments, 70:1-7 [8] Mathur N, Bhatnagar P, Bakre P (2006) Assessing mutagenicity of tannery dyes from Pali (Rajasthan) using Ames bioassay. Appl Ecol Environ Res, 4(1):111 - 118. [9] Puvaneswari N, Muthukrishnan J, Gunasekaran P (2006) Toxicity assessment and microbial degradation of azodyes. Ind J Exp Biol, 44:618- 626. [10] Ponraj.M,Gokila.K,and Zambare Vasudeo(2011).Bacterial decolorization of textile Dye –Orange 3R.International Journal of advanced Biotechnology and Research.,2(1)168- 177 [11] Sasaki K, Sakai M, Matusita K, Masuda Y, Sato K (2008) Chemical structure analysis for azo type disperse dyes by mass spectroscopy and detection of dyestuff in tannery products causing allergic contact dermatitis. The Jap Soc Analyt Chem: Bunseki Kagaku, 57: 833-850. [12] Saunders H, O Brien T, Nixon R (2004) Tannery dye allergic contact dermatitis following paraphenylenediamine sensitization from a temporary tattoo. Aus J Dermatol, 45(4):229 - 231. [13] Shitole VH, Panvalkar SS (2000) Bioremediation of tannery effluent. J Emp Bio, 1(2):10.. [14] Tufekci N, Sivri N, Toroz I (2007) Pollutants of tannery industry wastewater and assessment of its discharge limits by water quality standards. Turk J Fish Aquat Sci, 7(2): 97- 103. [15] Vilaseca M, Gutie MC, Grimau VL, Mesas ML, Crespi M (2010) Biological treatment of a tannery effluent after electrochemical oxidation of reactive dyes. Water Environ Res, 82(2):176-182. DOI: [16] Wong PK, Yuen, PY (1996) Decolourization of synthetic dyes by Klebsiella pneumoniae RS- 13. Water Res, 30: 1736-1744. [17] Yusuff RO, Sonibare JA (2004) Characterization of tannery industries effluents in Kaduna, Nigeria and pollution implications. Global Nest: The Int J, 6(3): 212 -221. 0 10 20 30 40 50 60 70 %Decolorization Dyes 2 4 6 8 10