Biodegradation of Black Liquor
B.G. Gaikwad*
C.E. Division, National Chemical
Laboratory, Pune-411008
*Corresponding Author E-mail: bg.gaikwad@ncl.res.in
ABSTRACT:
Bacterial strains and yeast strains were
screened for treatment of black liquor. 17 bacterial cultures of genus –arthrobacter, cellulomonas, chainia, pseudomonas
and glucanobacter were used. 19 yeast cultures
having genus- kluyveromyces, pachysolen,
pichia, rhodotorula, saccharomyces, candida and yerrowia were used
for study. At pH 8.0, 58.33% sugar
utilization, 16.14% phenol degradation, 37.81% decolorization
was obtained by using Candida catanula NCIM 3337, C. brumptii 3402, Pseudomonas fluorescens
2653 respectively. 45.63% sugar
utilization, 29.48% phenol degradation ,
20.97% decolorization
was observed by using Yerrowia lipolytica NCIM 3472,
Pseudomonas fluorescens
2173, Yerrowia lipolytica 3589 respectively at pH 6.5. 63.49% sugar
utilization was observed by Pseudomonas fluorescens 2141 at pH 4.5. 28.85% phenol degradation
was done by Pachysolen tannophilus 3445 at pH 4.5. 63.26% decolorization
was observed for Candida lambica 3532 at pH 4.5. Use of biomass for decolorization was attempted in this study. Fermentation of
fruits was carried out. Sapota, fig, papaya, pineapple, banana, guava and
tamarind were used for fermentation. Fermentation was done by using
baker’s yeast. Residue from ethanol
fermentation was used for decolorization of black
liquor. Decolorization was obtained by residue from
banana and tamarind fermentation residue was higher. It was 63.79 and 65.62% decolorization for
banana and tamarind fermentation residue respectively.
KEYWORDS: Decolorization,
candida, sugar, phenol, pH, pseudomonas etc.
INTRODUCTION:
Pollution from different industries is
harmful for environment. Pollution from paper and pulp industry is a major
problem, which is required to be resolved successfully Effluent from paper and
pulp industry is called black liquor. It is also termed as sulphite
waste liquor. Color and hazardous chemicals in black liquor are dangerous to
aquatic livings. It can be used for drinking and other purpose. Many years
researchers are working to solve it but still successful technology is in
waiting list., Chai et al. (2014)1 ,
Chandra and Abhishek (2011)2, Oliveira et
al. (2009)3, Jin (2008)4,
Chandra et al. (2007)5 etc.
have studied decolorization of BL. It is mentioned in
results and discussions. Some researchers have studied use of biomass for color
removal.
In this study we have reported here
screening of strains for treatment of black liquor. Use of biomass for color
removal is attempted in this work. Study has shown that it is possible to
reduce pollution.
MATERIALS AND METHODS:
Chemicals and
Cultures
Chemicals from Hi-Media, Mumbai and S.D.
Fine Chemicals, Mumbai were used for experiment. Cultures were brought from
NCIM (National Collection of Industrial Microorganism), Pune.
Baker’s yeast was purchased from Local purchase.
Growth
Bacterial cultures were maintained on
Nutrient –agar medium (beef extract 10, NaCl 5,
peptone 10 g/L, pH 7.0, agar 20g/L.) at 40C. Yeast cultures were
maintained on MGYP-agar (Malt extract 0.3, glucose 1, yeast extract 0.3 and
Peptone 0.5 %, pH adjusted to 6.5. 2.0%
agar used). Bacterial cultures were
grown on nutrient broth. Yeast cultures were grown on MGYP. Preinoculum
was used for growth. Growth was carrried out at 280C,
220 rpm for 24h. Cells were centrifuged and used for study.
Sugar was determined by DNSA
method (Miller 1959)6. Nitroprusside
method was used for phenol determination [Rodenas-Torralba
et al. (2005)]7. Colour was measured at
465nm [Chandra and Abhishek (2011)]2 at pH
8.0 and 6.5 study. While for pH 4.5, we have used wavelength 700nm.
Biodegradation:
1mL cell slurry was taken. 4mL 1:5 diluted
black liquor (BL) was added. Cell concentration was 2.5%. pH of diluted BL was
as per policy decided. It is kept at 280C, 220rpm for 24 h. Sugar,
phenol and colour was determined.
Experimental:
Screening of cultures
We have used 17 bacterial and 19 yeast
cultures for screening study. List of cultures used is given in table 1. Study
was performed using diluted (1:5) BL with different pH i.e. 8.0, 6.5 and 4.5.
Results obtained were screened. We have selected 3 cultures showing which show
maximum sugar utilization, phenol degradation and decolorization
from each pH study. Results are shown in table 2-4. Use fermentation residue Fruits were
fermented. Banana, grape, guava, sapota, fig, papaya,
pineapple, and tamarind were used. Sugar concentration was 10-15%. Volume was
25mL. 2.5% baker’s yeast was used.
Fermentation mixture was centrifuged after 24h and residue was collected.
Residue contains yeast and fruit debris. This is used for removal of colour. Residue equivalent to 2.5% baker’s yeast was used
for decolorization of. 20mL 1:5 diluted black liquor
pH 4.5. It was stirred till decolorization and decolorization was measured.
RESULTS AND DISCUSSION:
We have done study at different pH i.e.
8.0, 6.5 and 4.5. Cultures having maximum results are discussed.
Biodegradation at
pH 8.0:
We found Candida catenula NCIM 3337 has ulitized
maximum sugar i.e. 58.33%. Candida brumptii 3402 degraded 16.14% phenol. Pseudomonas fluorescens
2653 has shown 37.81% decolorization (table 2).
Table
1: List of cultures
|
Genus |
Culture and NCIM no. |
Numbers of cultures |
|
Arthrobactrer |
Arthrobacter sp. 2934, 2935, 2937, 2938 |
4 |
|
Candida |
C. lambica 3532, C. epicola 3367, C. glabrata 3237, C. catenulata 3337, C. bombi 3531,
C. brumptii
3402 |
6 |
|
Cellulomonas |
C. flavigena
2481 |
1 |
|
Chainia |
Chainia sp. 2980 |
1 |
|
Gluconobacter |
G. roseus 2524 |
1 |
|
Kluyveromyces |
K. marxianus 3232, 3465 |
2 |
|
Pachysolen |
P. tannophilus 3502, 3445 |
2 |
|
Pichia |
P. guilliermondii 3251, P.
farinosa 3461, P. stipitis 3498 |
3 |
|
Pseudomonus |
P. fluorescens (5164, 2653, 2099, 2100, 2141,
2173); P. pictorum
2077; P. cruciviae
2004; P. sp. 2223, 2303 |
10 |
|
Rhodotorula |
R. glutinis
3170 |
1 |
|
Saccharomyces |
S. cerevisiae 3523, 3524, 3262 |
3 |
|
Yarrowia |
Y. lipolytica 3472, 3589 |
2 |
Table
2:
Biodegradation of BL at pH 8.0
|
Culture |
NCIM
no |
Biodegradation
% |
||
|
Sugar
utilization % |
Phenol
degradation % |
Decolorization % |
||
|
Candida catenulata |
3337 |
58.33 |
12.23 |
0 |
|
Saccharomyces cerevisiae |
3524 |
54.21 |
0 |
7.17 |
|
Pachysolen tannophilus |
3445 |
50.60 |
0 |
0 |
|
Candida brumptii |
3402 |
29.16 |
16.14 |
0 |
|
Candida
lambica |
3532 |
0 |
15.62 |
0 |
|
Candida bombii |
3531 |
20.83 |
14.06 |
9.58 |
|
Pseudomonus fluorescens |
5164 |
31.81 |
0 |
19.53 |
|
Pseudomonus fluorescens |
2653 |
0 |
0 |
37.81 |
|
Saccharomyces cerevisiae |
3523 |
36.14 |
0 |
19.55 |
Table 3: Biodegradation of BL at pH 6.5
|
Culture |
NCIM no |
Biodegradation % |
||
|
Sugar utilization % |
Phenol degradation % |
Decolorization % |
||
|
Arthrobacter sp. |
2934 |
40 |
0 |
0 |
|
Pichia guilliermondii |
3251 |
42.71 |
11.46 |
4.13 |
|
Yerrowia lipolytica |
3472 |
45.63 |
12.64 |
0 |
|
Pseudomonus fluorescens |
2173 |
0 |
29.48 |
0 |
|
Candida bombii |
3531 |
0 |
19.26 |
0 |
|
Candida epicola |
3367 |
30.09 |
17.78 |
0 |
|
Yerrowia lipolytica |
3589 |
40 |
0 |
20.97 |
|
Pseudomonus fluorescens |
2653 |
0 |
0 |
9.27 |
|
Pseudomonus fluorescens |
5164 |
5.77 |
0 |
6.7 |
Biodegradation at
pH 6.5:
Yerrowia lipolytica 3472
ulitized 45.63%
sugar at pH 6.5. Pseudomonas fluorescens
2173 degraded 29.48% phenol. Yerrowia lipolytica 3589 had 20.97 % decolorization
(table 3).
Biodegradation at
pH 4.5:
Results from table 4 shows that Pseudomonas fluorescens
2141: 63.49% sugar utilization; Pachysolen tannophilus 3445: 28.85% phenol degradation and 63.26% decolorization by Candida
lambica 3532. Results of sugar utilization and decolorization are lower at pH 6.5. Phenol degradation is
more at pH 6.5. Comparison of maximum biodegradation obtained at different pH
is in figure 1. Overall we achieved 63.49% sugar utilization by Pseudomonas fluorescens
2141 at pH 4.5; 29.48% phenol degradation by Pseudomonas fluorescens 2173 at pH 6.5 and
63.26% decolorization by Candida lambica 3532 at pH 4.5.
Figure 1: Comparison of
biodegradation at different pH: Parameters on X-axis are S-sugar utilization; P-phenol degradation ; D- decolorization.
Sugar
utilization(S): B- Candida catenula 3337-pH 8.0; C-Pseudomonas fluorescens 2141-pH- 4.5
Phenol
degradation (P): D-Candida brumptii 3402-pH 8.0; E- Pseudomonas fluorescens 2173-
pH
6.5; F-Pachysolan tannophilus
3445-pH4.5
Decolorization (D): G- Pseudomonas fluorescens 2653-pH 8.0; H-Candida lambica 3532-pH 4.5
Table 4: Biodegradation of BL at pH 4.5
|
Culture |
NCIM no |
Biodegrdation % |
||
|
Sugar utilization % |
Phenol degradation % |
Decolorization % |
||
|
Pseudomonus fluorescens |
2141 |
63.49 |
15.59 |
18.10 |
|
Pseudomonus sp. |
2303 |
57.14 |
0 |
53.44 |
|
Arthrobacter sp. |
2934 |
55.55 |
0 |
50 |
|
Pachysolen tannophilus |
3445 |
0 |
28.85 |
39.79 |
|
Saccharomyces cerevisiae |
3262 |
0 |
24.47 |
57.14 |
|
Candida glabrata |
3237 |
0 |
24.16 |
5.43 |
|
Candida lambica |
3532 |
0 |
9.52 |
63.26 |
|
Candida catenulata |
3337 |
28.57 |
0 |
59.48 |
|
Pichia guilliermondii |
3251 |
27.27 |
0 |
62.93 |
Figure
2: Comparison of decolorization
by residue of fruit fermentation:
B-Sapota; C-fig; D-papaya;
E-pineapple; F-banana; G- guava; H-tamarind
Results at lower pH are higher. Maximum decolorization was observed at pH 4.5. Candida lambica 3532 has shown highest decolorization. 79% decolorization
was observed in 144h
using bacteria by Chandra and Abhishek (2011)2.
Comamonas sp. B-9 has done 54% color reduction
in 7days [Chai et al. (2014)]1. Zheng et. al. (2014)8 has reported 35.3% decolorization
by Comamonas sp. B-9. Bacillus pumilus
CBMAI 0008 has shown 41.87% decolorization, whereas Paenibacillus
sp. CBMAI 868 has shown 42.3% decolorization
[Oliveira et al. (2009)]3. Chandra et al. (2007)5 have
studied decolorization by mixed bacterial cultures.
They reported 69% decolorization. Jin (2008)4 removed 93.15% color of BL using Aspergillus fumigatus
JX-5.
Fermentation of fruits was carried out.
Fermentation residue was used decolorization of 1:5
diluted black liquor pH 4.5. Results are presented in figure 2. It shows banana
and tamarind fermentation residues have more decolorization.
Maximum decolorization (65.62%) was observed by using tamarind fermentation residue. Clear liquid is obtained by treatment. This
is due to adsorption of colored matter on yeast and fruit debris. Wang and Guo (2011)9 used beer yeast sludge for removal
of color of dye. Biomass from amino acid fermentation was used for removal of
color of dye by some researchers [Won et al. (2006)10; Vijayraghavan and Yun (2007)11].
In our study we have used biomass and fruit debris to adsorb
the coloring constituents. As some
fruits contain pectin, which is sticky in nature, may help in attaching colouring matter. This will help in removing colour more effectively than only cells itself. The
present work will
be useful in
developing feasible technology
at higher scale
where patent can be developed.
CONCLUSION:
Candida lambica NCIM 3532 has shown 63.26 % decolorization
of 1:5 diluted black liquor at pH 4.5. This culture is best culture. Among
fermentation residue study, we observed banana and tamarind are good. Tamarind
has shown 65.62 % decolorization which is highest
among the fruits used. Clear liquid is obtained by these two approaches.
REFERENCES:
1. Chai
LY, Chen YH, Tang CJ, Yang ZH, Zheng Y and Shi Y. Depolymerization and decolorization
of kraft lignin by bacterium Comamonas
sp. B-9. Applied
Microbiology and Biotechnology
98(4); 2014:
1907-1912.
2. Chandra R and Abhishek A. Bacterial decolorization of black liquor in axenic
and mixed condition and characterization of metabolites. Biodegradation 22;
2011: 603–611.
3.
Oliveira PL, Duarte MCT, Ponezi AN and Durrant LR. Use of Bacillus pumilus
CBMAI 0008 and Paenibacillus sp. CBMAI 868 for colour removal from paper mill effluent. Brazilian Journal
of Microbiology 40; 2009: 354–357.
4. Jin XC. Research on treating black liquor of straw pulp with strain JX-5. Jiangxi Shifan
Daxue Xuebao Ziran Kexueban 32(5); 2008:
555-558 (Chinese) [CAN 151:455069].
5.
Chandra R, Raj A, Purohit HJ and Kapley A. Characterisation
and optimisation of three potential aerobic bacterial
strains for kraft lignin degradation from pulp paper
waste. Chemosphere 67; 2007: 839–846.
6. Miller GL. Use
of dinitrosalicylic acid
reagent for determination
of reducing sugar. Analytical Chemistry 31(3); 1959:
426-428.
7. Rodenas-Torralba E, Morales-Rubio A and Guardia
Miguel de la. Determination of phenols
in waters using micro-pumped multicommutation and
spectrophotometric detection: an automated alternative to the standard
procedure. Analytical and Bioanalytical Chemistry.
383; 2005: 138–144.
8.
Zheng Y, Chai LY, Yang
ZH, Chen YH, Shi Y and Wang YY. (2014) Environmentally safe treatment of black
liquor with Comamonas sp. B-9 under high-alkaline
conditions. Journal of Basic microbiology 54; 2014: 152-161
9.
Wang Baoe
and Guo Xiu. Reuse of waste beer yeast sludge for biosorptive decolorization of
reactive blue 49 from aqueous solution. World Journal of Microbiolology and
Biotechnology 27; 2011:1297–1302.
10.
Won SW, Kim HJ, Choi SH, Chung BW, Kim
KJ and Yun YS.
Performance, kinetics and equilibrium in biosorption
of anionic dye reactive black 5 by the waste biomass of Corynebacterium
glutamicum as a low-cost biosorbent.
Chemical Engineering Journal 121; 2006:37–43.
11.
Vijayaraghavan
K and Yun YS. Utilization of fermentation
waste (Corynebacterium glutamicum)
for biosorption of reactive black 5 from aqueous
solution. Journal of Hazardous Materials 141; 2007:45–52.
Received
on 29.12.2014 Modified on 10.01.2015
Accepted
on 22.01.2015 ©A&V Publications All right reserved
Research J. Science and Tech. 7(1):
Jan.-Mar. 2015; Page 47-51
DOI: 10.5958/2349-2988.2015.00008.X