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.

Analysis:

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