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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)
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Studies on the implication of distillery spentwash on the sustainability of tilapia fishes (Oreochromis niloticus)

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.

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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)

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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. Figure 1: Indicate Mortality rate, No of fish exposed, concentration of   PTSW, No of fish dead.

 

Click here to View figure

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.

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