Manuscript accepted on :
Published online on: --
S. Chandraju1*, L. Mohan Kumar1 and C.S. Chidan Kumar2*
1Department of Studies in Sugar Technology, Sir M. Vishweshwarayya Post- Graduate Centre, University of Mysore, Tubinakere, Mandya - 571 402, India.
2Department of Engineering Chemistry, Alva's Institute of Engineering and Technology, Mijar, Moodbidri - 574 225, Karnataka, India.
Corresponding Author E-mail: chandraju1@yahoo.com
DOI : http://dx.doi.org/http://dx.doi.org/10.13005/bbra/1066
ABSTRACT:
Management and conservation of Tilapia fishes was made with different concentration of primary treated spentwash (PTSW) (0.1% to 2.2%) in water. Spentwash was analyzed for its physico-chemical parameters. Fingerlings fishes (obtained from V.C. Farm, Mandya, Karnataka), were divided into 23 groups (G1 to G23) of 12each and keeping G1 as control unit, G2 to G23 were exposed to different concentrations of primary treated spentwash for a period of 6 days in different aquariums of 36" x 15" x 18" size. It was
KEYWORDS: Tilapia Fishes; Sustainability; Distillery Spentwash; Aquarium; Mortality Rate.
Copy the following to cite this article: Chandraju S, Kumar L. M, Kumar C. S. C. Studies on the implication of distillery spentwash on the sustainability of tilapia fishes (Oreochromis niloticus). Biosci Biotech Res Asia 2012;9(2) |
Copy the following to cite this URL: Chandraju S, Kumar L. M, Kumar C. S. C. Studies on the implication of distillery spentwash on the sustainability of tilapia fishes (Oreochromis niloticus). Biosci Biotech Res Asia 2012;9(2). Available from: https://www.biotech-asia.org/?p=10129 |
Introduction
Molasses (one of the important by- products of sugar industry) is the chief source for production of ethanol by fermentation method. In the year 1999, there were 285 distilleries in India producing 2.7 x 109 l of alcohol and generating 4 x 1010 l of wastewater each year1. This number has gone up to 319, producing 3.25 x 109 l of alcohol and generating 40.4 x 1010 l of wastewater annually 2. For every liter of ethanol production emerges about 8 liters of waste water called as raw spentwash (RSW). This RSW is known for high BOD (5000-8000mg/L) and COD (25000-30000mg/L)3, undesirable color due to the presence of water soluble recalcitrant coloring compound called melanoidin4 and foul odor5. Besides a number of pathological pollutants. The chief among the notable pollutants, is melanoidin pigment which is brown in color that stains the superficial water sheet and in turn cuts off the light rays and dulls photosynthesis when RSW is let into water bodies (tanks, lakes, channels, Ponds, etc). The brown ting of melanoidin pigment is the outcome of mailard reaction between sugar and amino compounds9. The RSW contains pyrogenic compound like polycyclic aromatic hydrocarbons (PAHS) and benzo (a) pyrene, a known environmental carcinogen 10-16.RSW is highly acidic and contains easily oxidizable organic matter with very high BOD and COD, this untreated RSW is let into water courses could definitely cause a great strain on aquatic life. But by installing biomethonation plant in distilleries would positively reduces oxygen demand of RSW. Thus, the resulting spentwash is known as primary treated spentwash (PTSW). Even though, PTSW has adverse effect on the aquatic life.
Tilapia fish is originated from Nile valley and spread to entire globe. This group of fishes can be cultured under very basic conditions and is ideal for rural subsistence farming, yet is minimal management and energy inputs. These fish have high reproductive and growth rates, are relatively disease free and hardy in nature.
Tilapia is the fifth most important fish in farming with production reaching 1,505,804 metric tons.17 Because of their large size, rapid growth, and palatability, tilapia are focus of major farming. Like other variety of fishes, tilapia are a good source of protein and also tilapia have very low levels of mercury18 as they are fast growing and short lived with a primarily herbivorous diet and thus do not accumulate mercury found in prey 19. Tilapia has low saturated fat, low calorie, low carbohydrate and low sodium protein source. It is a source of phosphorus, niacin, selenium, vitamin B12 and potassium. Tilapia is unable to survive in low temperature climates because they require warm water.
As a part of our ongoing studies of implication of distillery spent wash on the aquatic life20 the present work is focused on the study of life sustainability of tilapia fishes (Oreochromis niloticus) on exposure to different concentrations of PTSW.
Material and Methods
Physico chemical parameters of PTSW (100%, 0.1%, 0.2%, 0.3%, 0.4%, 0.5%, 0.6%,.7%,0.8%,0.9%,1.0%,1.1%,1.2%,1.3%1.4%,1.5%,1.6%,1.7%,1.8%1.9%,2.0%2.1%,2.2%) were analyzed by standard methods (Table 1). Two hundred and seventy six tilapia finger ling fishes obtained from G.K.V.K Bangalore, Karnataka and divided into 23 groups, and were set in aquarium of 36” x 15” x 18” size. These were exposed to different concentration of PTSW (0.1% to 2.2%) with normal feeding. G1 was kept as control unit. The mortality rate (MR) was recorded in each case up to 6 days of exposure (Table 2).
Results and Discussion
In G23 (2.2% PTSW) the MR was 100% after 12h exposure,50% in G22 (2.1%PTSW) and 16% in G21(2.0%PTSW) It was found that MR differs for G23, where as from G1 to G20 the MR was zero even after exposure for 6 days (Fig 1). The higher MR was noticed in G23 at higher concentration of PTSW with insufficient dissolved oxygen (DO). But in G1 to G20, DO was sufficient for respiration of the fishes as such they behaved normally and in higher concentration of PTSW fishes get disturbed and were swimming rapidly with random moment . A thick coat of mucus was observed all over the body of the fishes making the fish slimier21-23.The fishes was swimming with belly upward and zig-zag motion. There were also erratic and parallel movements observed in fish, indicating the loss of equilibrium.
Table 1: Physico-chemical parameters of different dilutions of spentwash
Parameters | 100%
PTSW |
0.1%
PTSW |
0.2%
PTSW |
0.3%
PTSW |
0.4%
PTSW |
0.5%
PTSW |
0.6%
PTSW |
0.7%
PTSW |
0.8%
PTSW |
0.9%
PTSW |
1.0%
PTSW |
1.1%
PTSW |
1.2%
PTSW |
pH | 7.57 | 7.62 | 7.60 | 7.56 | 7.49 | 7.86 | 7.94 | 7.96 | 7.98 | 7.80 | 7.98 | 7.80 | `7.96 |
EC | 40264 | 500 | 570 | 575 | 586 | 598 | 670 | 690 | 726 | 815 | 886 | 905 | 925 |
TS | 49116 | 220 | 250 | 285 | 292 | 320 | 390 | 435 | 534 | 624 | 688 | 710 | 724 |
TDS | 471323 | 290 | 320 | 360 | 364 | 400 | 480 | 530 | 608 | 640 | 696 | 720 | 780 |
TSS | 1984 | 6 | 7 | 7.5 | 8 | 9 | 1.0 | 11 | 12 | 13 | 14 | 15 | 16 |
Setteleable Solids | – | – | – | – | – | – | – | – | – | – | – | – | – |
COD | 38692 | 120 | 140 | 160 | 189 | 200 | 230 | 260 | 300 | 350 | 400 | 450 | 500 |
BOD | 28476 | 100 | 110 | 120 | 130 | 140 | 150 | 160 | 170 | 180 | 190 | 200 | 240 |
Carbonates | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Bi-Carbonates | 14126 | 192 | 192 | 192 | 193 | 194 | 194 | 195 | 196 | 196 | 196 | 196 | 196 |
Total P | 24.28 | 16.2 | 17.2 | 18.0 | 18.5 | 19.0 | 19.2 | 19.6 | 20.2 | 21.1 | 22.2 | 28.2 | 32.4 |
Total K | 5240 | 5.2 | 5.7 | 6.1 | 6.8 | 7.0 | 7.9 | 8.1 | 8.4 | 9.2 | 10.8 | 11.6 | 12.2 |
Calcium | 510 | 165 | 170 | 175 | 180 | 185 | 190 | 195 | 200 | 206 | 210 | 216 | 220 |
Magnesium | 1922 | 19.8 | 21.0 | 21.5 | 22.0 | 22.5 | 23.0 | 23.5 | 24 | 25 | 26 | 27 | 28 |
Sulphur | – | – | – | – | – | – | – | – | – | – | – | – | – |
Sodium | 210 | 19 | 20 | 21 | 21.5 | 22 | 24 | 26 | 28 | 30 | 32 | 34 | 36 |
chlorides | 6108 | 91 | 92 | 92 | 93 | 92 | 92 | 92 | 95 | 94 | 93 | 95 | 98 |
Iron | 19.32 | 0.4 | 0.4 | 0.4 | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 | 0.55 | 0.6 | 0.6 | 0.6 |
Manganese | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 |
Zinc | 0.35 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 |
Copper | – | – | – | – | – | – | – | – | – | – | – | – | – |
Cadmium | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Lead | 0.10 | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Chromium | 0.20 | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Nickel | 0.10 | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Ammonical Nitrogen | 1458 | 7.8 | 8.1 | 8.5 | 8.96 | 10.2 | 11.8 | 12.2 | 12.6 | 13.0 | 13.44 | 13.84 | 14.28
|
PTSW – Primary Treated spent wash
Table 1 Contd………
Parameters | 1.3%
PTSW |
1.4%
PTSW |
1.5%
PTSW |
1.6%
PTSW |
1.7%
PTSW |
1.8%
PTSW |
1.9%
PTSW |
2.0%
PTSW |
2.1%
PTSW |
2.2%
PTSW |
pH | 7.80 | 7.85 | 7.60 | 7.78 | 7.58 | 7.66 | 7.74 | 7.59 | 7.63 | 7.58 |
EC | 960 | 985 | 1015 | 1030 | 1055 | 1110 | 1145 | 1190 | 1210 | 1270 |
TS | 736 | 749 | 755 | 768 | 780 | 799 | 825 | 840 | 865 | 880 |
TDS | 803 | 820 | 844 | 860 | 895 | 936 | 974 | 997 | 1028 | 1056 |
TSS | 17 | 18 | 19 | 20 | 20 | 20.5 | 22 | 23 | 24 | 25 |
Setteleable Solids | – | – | – | – | – | – | – | – | – | – |
COD | 530 | 555 | 580 | 610 | 636 | 680 | 720 | 745 | 770 | 797 |
BOD | 260 | 295 | 330 | 400 | 420 | 470 | 505 | 600 | 620 | 640 |
Carbonates | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Bi-Carbonates | 220 | 220 | 228 | 229 | 234 | 240 | 250 | 255 | 252 | 266 |
Total P | 21.0 | 21.2 | 21.4 | 21.6 | 21.9 | 22.3 | 22.6 | 22.6 | 22.6 | 22.8 |
Total K | 13 | 13.8 | 14.3 | 14.9 | 15.8 | 15.9 | 16.9 | 17.8 | 18 | 18.9 |
Calcium | 225 | 228 | 232 | 236 | 240 | 243 | 245 | 248 | 248 | 249 |
Magnesium | 29 | 30 | 31 | 32 | 33 | 34 | 35 | 36 | 37 | 38 |
Sulphur | – | – | – | – | – | – | – | – | – | – |
Sodium | 37 | 39 | 40 | 41 | 41.5 | 42 | 43 | 44 | 45 | 46 |
chlorides | 98 | 99 | 103 | 106 | 103 | 108 | 104 | 109 | 110 | 109 |
Iron | 0.6 | 0.7 | 0.8 | 0.8 | 0.8 | 0.8 | 0.8 | 0.9 | 0.9 | 0.9 |
Manganese | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 | 0.2 |
Zinc | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 | 0.1 |
Copper | – | – | – | – | – | – | – | – | – | – |
Cadmium | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Lead | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Chromium | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Nickel | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL | BDL |
Ammonical Nitrogen | 14.98 | 15.60 | 15.88 | 15.99 | 16.30 | 16.40 | 16.80 | 16.99 | 17.80 | 17.95 |
PTSW – Primary Treated spentwash
Table 2: Mortality rate (%) of tilapia fish exposed to different dilutions of spentwash
Groups | No. of fish
exposed |
Concentration
PTSW (%) |
No of fish dead | No. of Fish survived
|
%
mortality |
G1 | 12 | 0.0 | 0 | 12 | 0 |
G2 | 12 | 0.1 | 0 | 12 | 0 |
G3 | 12 | 0.2 | 0 | 12 | 0 |
G4 | 12 | 0.3 | 0 | 12 | 0 |
G5 | 12 | 0.4 | 0 | 12 | 0 |
G6 | 12 | 0.5 | 0 | 12 | 0 |
G7 | 12 | 0.6 | 0 | 12 | 0 |
G8 | 12 | 0.7 | 0 | 12 | 0 |
G9 | 12 | 0.8 | 0 | 12 | 0 |
G10 | 12 | 0.9 | 0 | 12 | 0 |
G11 | 12 | 1.0 | 0 | 12 | 0 |
G12 | 12 | 1.1 | 0 | 12 | 0 |
G13 | 12 | 1.2 | 0 | 12 | 0 |
G14 | 12 | 1.3 | 0 | 12 | 0 |
G15 | 12 | 1,4 | 0 | 12 | 0 |
G16 | 12 | 1.5 | 0 | 12 | 0 |
G17 | 12 | 1.6 | 0 | 12 | 0 |
G18 | 12 | 1.7 | 0 | 12 | 0 |
G19 | 12 | 1.8 | 0 | 12 | 0 |
G20 | 12 | 1.9 | 0 | 12 | 0 |
G21 | 12 | 2.0 | 2 | 10 | 16 |
G22 | 12 | 2.1 | 6 | 6 | 50 |
G23 | 12 | 2.2 | 12 | 0 | 100 |
PTSW – Primary Treated spent wash
Figure 1: Indicate Mortality rate, No of fish exposed, concentration of PTSW, No of fish dead.
|
Conclusion
The discharge of distillery spent wash into water bodies at higher concentration leads to deficient of sunlight into water (due to dark brown color) and further the spent wash promotes mucus formation on the gills of the fishes. Hence, there is a reduction of oxygen tension in gills of fishes, which makes them behave abnormal due to insufficient dissolved oxygen and finally leads to death.
The present study revealed that, higher the concentration of distillery spent wash lead into water bodies, the more the depletion of tilapia fishes.
Acknowledgement
Authors are grateful to the General Manager, Nijaveedu Sugars Ltd., Koppa, Mandya, Karnataka for providing spentwash.
References
- Joshi, H .C. Bio-energy potential of distillery effluents. Bio. Energy News, 3: 10 15 (1999).
- Uppal, J. Water utilization and effluent treatment in the Indian alcohol industry – An overview. In: Liquid Assets, Proceedings of Indo-EU workshop on Promoting Efficient Water Use in Agro-based Industries. TERI Press, New Delhi, India. pp. 13-19. (2004).
- Joshi, H.C., Karl, N. Chaudhary, A. Deb, D.L.. Environmental issues related with distillery effluent utilization in agriculture in India, ASIA POC J. environ. Develop, 1: 92- 103 ( 1994).
- Evershed, R .P. Bland, H.A. Van Bergen, P.F. Carter, J .F. Horton, M.C . Rowley- Conway, P.A .,. Volatile compounds in archeological plant remains and the Maillard reaction during decay of organic matter. Science, 278: 432-433 (1997).
- Sirianuntapiboon,S. Zohsalam, P. Ohmomo, S. Decolorization of molasses waste water by Citromyces sp. WR-43-6.Process Biochemist, 35:917-924 (2004).
- Chandra, R., P.K. Pandey. Decolonization of anaerobically treated distillery effluen activated charcoal adsorption method. Indian J. Environ. Protection, 2: 132-134 (2001).
- Cerniglia, C. E. Sutherland, J. B. Crow, S. A.. Fungal metabolism of aromatic hydrocarbons In Microbial Degradation of Natural Products (G. Winkelmann, ed.) 194±217. VCH,Weinheim (1992).
- Urso,P. Gengozian, N. Alterations in the humoral immune response and tumor frequencies in mice exposed to benzo (a) pyrene and X-rays before or after birth. Journal of Toxicology and Environmental Health, 10: 817-835 (1982).
- Martins, S. I. F. S.Van Backel, M. A. J. S..A Kinetic model for the glucose|glycia mailard reactions pathways. Food Chem.: 90:257-269 (2004).
- Stein, J. Reichert, W. Nishimoto,M. Varanasi,U. Overview of studies on liver carcinogenesis in English sole from Puget Sound; Evidence for a xenobiotic chemical Etiology: Biochemical studies.Sci. Total Environ., 94: 51-69 (1990).
- Agarwal, C. S. Pandey, G. S. Soil Pollution by spentwash discharge: depletion of manganese (11) and impairment of its oxidation. J.Envirn.Biol., 15:49-53 (1994).
- Vethaak, A. Wester, P. Diseases of flounder Platicthys flesus in Dutch coastal and estuarine waters, with particular reference to environmental stress factors. Liver Histopathology Disease of Aquatic Organisms, 26: 99-119 (1996).
- Holladay, S.D. Smith, S.A., Besteman, E.G., Deyab, A.S.M.I., Gogal, R.M., Hrubec, T ., Robertson, J.L. Ahmed, S.A., Benzo(a) pyrene-induced hypocellularity of the pronephros in tilapia (Oreochromis niloticus) is accompanied by alterations in stromal and parenchymal cells and enhanced immune cell apoptosis. Vet. Immunology and Immunopathology, 64: 69-82 (1998).
- Shailaja, M.S . D’Siliva, C. Evaluation of impact of PAH on a tropical fish, Oreochromis mossambicus using multiple biomarkers. Chemosphere, 53: 835-841(2003).
- Raghukumar, C . Mohandass, C. Kamat, S . Shailaja, M.S. Simultaneous detoxification and decolorization of molasses spent wash by the immobilized white-rot fungus Flavodon flavus isolated from a marine habitat. Enzyme and Microbial Technology, 35: 197-202 (2004).
- Patil, J.D. Arabatti, S.V. Hapse, D.G. A review .of some aspect of distillery spentwash (vinase) utilization in sugarcane, Barathiya sugar, May; 1-15 (1987).
- Fessehaye, younas (PDF).Natural mating in Nile tilapia (oreochromis niloticus L.) implication for reproductive success, in breading, and cannibalism (2006).
- Mercury levels in commercial fish and shellfish http://www..cfsan,fda.gov/~frf/seamehg,html),USFDA<May2001;updated feburuary (2006)
- http://www.eattilapia.com /nutritional-facts.php
- Chandraju, S. Mohan Kumar, L. Chidankumar, C.S . Implication of Distillery Spentwash on the Sustainability of Common Carp (cyprinus carpio) Fishes, Bioresearch Bulletin, 3:161-165 (2010).
- Carpenter, K.E. On the biological factors involved in the destruction of river fisheries by pollution due lead mining. Ann Appl. Boil., 12(1):1-23 (1924).
- Carpenter, K.E. The lethal action of soluble metabolic salts on fishes. J.Expt.Boil., 4: 378-390 (1927).
- Durve , V. S.Jain, S . M . Toxicity of distillery effluent to the cyprinid weed fish Rasbora daniconius (Ham). Acta. Hydrochim., 8(4): 329-336 (1980).
This work is licensed under a Creative Commons Attribution 4.0 International License.