2. GERF Bulletin of Biosciences 2011, 2(2):29-31 30
Reducing sugar quantification by DNS method
Table 2: Effect of wood saw dust (WSD) fungal enzyme
One gm of 3, 5 Dinitro salicylic acid (DNS) was mixed and chemical treatment for saccharification for bio-energy
with 20 ml of 2 N NaOH. Thirty gm of sodium potassium production
tartrate was added and volume was made up to 100 ml.
Enzymatic and Autoclaved Un-Autoclaved
Substrate (0.4 ml) was taken in a fresh tube and 0.1 ml of gm % (w/v) gm% (w/v)
Chemical treatment
enzyme was added into it, then 1 ml of 3, 5 DNS was mixed in Control 0.60±0.05 0.07±0.03
the solution and kept in boiling water bath for 10 min. The Aspergillus fumigatus 1.69±0.01 1.32±0.04
samples were with drawn and cooled under running tap water. NaOH (1N) 0.57±0.02 0.072±0.02
Ten ml of distilled water was added and reading was taken at H2SO4(1N) 5.52±0.05 1.1±0.02
546 nm (Jurcoane et al., 2009).The amount of reducing sugar HCl(1N) 4.67±0.08 0.86±0.01
was determination as per method described by Sadasivam
and Manickam (1996). Values are presented as mean + standard deviation (n=3)
Results and Discussion
2 .5 0 1 4 .0 0
Enzyme hydrolysis from several fungal strains was tested.
Hydrolysis of Enzyme (mg/ml)
2 .2 01 2 .0 0
Hydrolysis with acid (mg/ml)
2 .0 0 1 1 .0 0
It was found that the values of the reducing sugars obtained 1 0 .0 0
1 .7 2
from the WSD are shown in Table 1. T. viride produced 1 .5 0 8 .0 0
7 .0 0
enzymes showed lowest value (0.022±0.002 g/l) for 6 .0 0
5 .0 9
hydrolysis as well as a saccharification and maximum 1 .0 0 4 .0 7 4 .0 0
saccharification was observed (0.119±0.136 g/l) with A. wentii 0 .7 2
2 .0 0
generated microbial enzyme. 0 .5 0 1 .3 0
0 .2 5 0 .4 1
0 .02 0 .0 0
0 .1 3
Treatment with 1 N H2SO4 after A. fumigatus extracellular 0 .0 0 0 .03 0 .0 5 -2 .0 0
0 1 3 5 7 17 21
enzymatic hydrolysis showed higher value (0.99±0.001g/l).
Tim e Inter va l (hour)
It increases 24% more than enzymatic saccharification. Most
En zym e Su lfu ric a cid
lignocellulosic wastes, due to the presence of cellulose
crystallinity, the chemical attack on the cellulose is retarded Fig1: Effect of enzyme and sulfuric acid on hydrolysis of
(Mosier et al., 2002). Therefore, chemical pretreatment was wood saw at dust different time interval.
necessary to increase the susceptibility of lignocellulose for
hydrolysis reaction. Chemical treatment may accelerate the significant effect for saccharification in horticulture waste.
rate of reaction and the extent of cellulose hydrolysis Earlier (Nzelibe et al., 2007) also reported that sulfuric acid
(Najafpour et al., 2007). hydrolysis was better than alkaline hydrolysis. Perhaps WSD
waste might have high cellulose and hemicellulose contents
Table1: Effect of wood saw dust (WSD) fungal enzyme and low lignin content. Enzyme is placed beneath the network
and chemical treatment for saccharification. of lignin and hemicellulose components. Pretreatment or
hydrolysis with sulphuric acid might have removed and
Hydrolysis of wood saw dust Sugar gm% hydrolysed hemicellulose to their monomeric constituent
waste (WSD) and lignin hemicellulose cellulose interactions partially
Aspergillus fumigatus 0.024±0.001 disrupted. Compared to acid hydrolysis 11.0±0.75 g/l was
Rhizopus 0.026±0.005 found better than enzyme hydrolysis (2.20±0.08 g/l) in Fig.1.
Trichoderma viride 0.022±0.002 This showed acid hydrolysis significantly (P<0.01) enhanced
Aspergillus wenti 0.119±0.136 saccharification of saw dust waste. Increasing their
Aspergillus fumigatus+ HCl (1N) 0.990±0.001 concentration (1, 3 and 5 N) sulfuric acid lowered hydrolysis
Rhizopus+ HCl (1N) 0.893±0.001 (7.7±0.1 g/l) at unautoclaved condition but maximum
Trichoderma viride+ HCl (1N) 0.025±0.002 hydrolysis was found same concentration (1 N sulfuric acid)
Aspergillus wenti+ HCl (1N) 0.029±0.003 at autoclaved condition (23.4375±0.2 g/l) and 5 N sulfuric
Values are presented as mean + standard deviation (n=3) acid does not shows any significant result for hydrolysis
By comparison of enzyme and chemical hydrolysis, it was compared to low acid concentration (1N and 3 N). As clearly
found that autoclaved enzyme treatment followed by stated by the numbers, the sugar concentration was
sulphuric acid hydrolysis resulted in maximum saccharifica- increased with an increase in the acid concentration that
tion (5.52±0.05 g/l) in Table 2. It was approximate increase of was applicable to the acid, catalyzed the hydrolysis process.
5% than unautoclaved but sodium hydroxide showed no The catalyst activity was proportional to H+ concentration.
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3. 31 GERF Bulletin of Biosciences 2011, 2(2):29-31
The more hydrogen ions formed in the solution, the more hydrolysis of pretreated palm oil lignocellulosic
rapid the hydrolysis process occurred (Mosier et al., 2002). wastes. IJE Transactions. 20(2): 147-156.
Aonla pomace was used as strong hydrolyser because it 9. Nzelibe HC and Okafoagu CU (2007). Optimization
was acidic in pH (>2) which help saccharification of wood. of ethanol production from Garcinia kola (bitter
The WSD hydrolyzed with extracellular enzyme, dilute kola) pulp agrowaste. Afr. J. Biotechnol. 6(17):
sulfuric acid (1 N) and aonla pomace waste as hydrolyser 2033-2037.
produced sugars, 3.28, 23.11 and 2.61 g/l, respectively. It’s 10. Sadasivam S and Manickam A (1996). Biochemical
showed 11.29% hydrolysis compared to dilute sulfuric acid. Methods, New Age. International Publishers (P)
Ltd., New Delhi, India.
Conclusion 11. Vintila T, Dragomirescu M, Croitoriu V, Vintila C,
Barbu H and Sand C (2010 ). Saccharification of
This study revealed that WSD was hydrolyzed at 1.69 g/ lignocellulose using different cellulases. Romanian
l, using a A fumigatus extracted crude culture filtrate at pH Biotechnol. Lett. 15(4): 5498-5504.
5.0, 30 ºC in acetate buffer 50 mM, while when using 1 N
sulfuric acid at a temperature of 121ºC for 20 min, was 23.3 g/
l but in 5 N there was no significant effect. This study also
suggested that aonla pomace waste could be used as
hydrolyser.
Reference
1. Akin-Osanaiye BC, Nzelibe HC and Agbaji AS
(2005). Production of ethanol from Carica papaya
(pawpaw) agro waste: effect of saccharification and
different treatments on ethanol yield. Afr. J.
Biotechnol. 4(7): 657-659.
2. Badger PC (2002). Ethanol from cellulose: A general
review. In: Trends in new crops and new uses (Eds.
Janick J. and Whipkey A.). ASHS Press,
Alexandria., pp. 17-21.
3. Baig MMV, Baig MLB, Baig MIA and Yasmeen M
(2004). Saccharification of banana agro-waste by
cellulolytic enzymes. Afr. J. Biotechnol. 3(9): 447-
450.
4. Chandel AK, Chan ES, Rudravaram R, Narasu, Rao
LV and Ravindra P (2007). Economics and
environmental impact of bioethanol production
technologies: An appraisal. Biotechnol. Mol. Bio.
Rev. 2(1): 14-32.
5. Jurcoane S, Radoi-Matei F, Toma R, Stelian P,
Vintiloiu A and Diguta C (2009). Hydrolysis of
agricultural biomass by combined pretreatment and
enzymatic methods in order to produce biofuels
(ethanol, biogas). Zootehnie si Biotehnol. 42(1):
58-63.
6. Karmakar M and Ray RR (2011). Saccharification of
agro wastes by the endoglucanase of Rhizopus
oryzae. Ann. Bio. Rech. 2(1): 20-208.
7. Mosier NS, Ladisch CM and Ladich MR (2002).
Characterization of acid catalytic domains for
cellulosehydrolysis and glucose degradation.
Biotechnol. Bioeng. 79(6): 610-618.
8. Najafpour G, Ideris A, and Salmanpour S (2007). Acid
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