MEKARN Conference 2010 |
A study was conducted to determine two methods of treating the wastewater from pig farm by draining directly to a fish pond or biodigester followed a fish pond and to evaluate the effect of the pig number per unit of water surface on the water quality. Quality of water was evaluated by using parameters of temperature, pH, dissolved oxygen (DO), chemical oxygen demand (COD), biochemical oxygen demand (BOD5), suspended solids (SS), total nitrogen, total phosphorus, total Coliforms and parasitic eggs. The results show that the model of biodigester followed the fish pond was more effectively and the quality of the wastewater in the fish pond met the government standards and reached type A (Vietnam Standard: TCVN 5945 – 2005). For the first model, the pig number of 2.25/100m2 water surface was more effectively than that of 5.33/100m2. For the second model, the pig number of 4.5/m3 biodigester and 5.4 pig/100m2 water surface are more effectively than that of 19.7 and 9.12, respectively. The wastewater pig can be solved by using bio-treating methods, the model of biodigester followed the fish pond is more effectively.
Experimental design:
1. A model of fish pond
Table 1. Number of pigs/ water surface
|
Pig heads |
Pig head/100m2 water surface |
Treat 1 |
32 |
5.33 |
Treat 2 |
33 |
2.35 |
2. A biodigester followed a fish pond
Table 2. Number of pigs/biodigester and fish pond
|
Pig head |
Biodigester (m3) |
Fish pond (m2) |
Pig head/m3 biodigester |
Pig head/100m2 water surface |
Treat 3 |
985 |
50 |
10800 |
19.7 |
9.12 |
Treat 4 |
227 |
50 |
4200 |
4.54 |
5.4 |
Results
Table 1. Effect of treating waste water of the model of fish pond
Pig head/100 m2 water surface |
From pig pen |
Fish pond |
P |
Temperature, oC |
|||
5.33 |
28.33a |
29.92b |
<0.01 |
2.35 |
28.67a |
29.75b |
<0.01 |
pH |
|||
5.33 |
7.40a |
6.72b |
<0.01 |
2.35 |
7.37a |
6.92b |
<0.01 |
DO, mg/l |
|||
5.33 |
0.00a |
1.43b |
<0.01 |
2.35 |
0.00a |
3.135b |
<0.01 |
BOD5, mg/l |
|||
5.33 |
957.60a |
72.53b |
<0.01 |
2.35 |
877.33a |
72.67b |
<0.01 |
COD, mg/l |
|||
5.33 |
1650a |
98.67b |
<0.01 |
2.35 |
28.67a |
72.67b |
<0.01 |
SS, mg/l |
|||
5.33 |
1350a |
116.67b |
<0.01 |
2.35 |
1350a |
88.33b |
<0.01 |
Nitrogen, mg/l |
|||
5.33 |
54.36a |
8.46b |
<0.01 |
2.35 |
50.45a |
7.84b |
<0.01 |
Phosphorus, mg/l |
|||
5.33 |
329.99a |
41.86b |
<0.01 |
2.35 |
295.54a |
25.38b |
<0.01 |
Parasites, egg/l |
|||
5.33 |
9.00a |
0.00b |
<0.01 |
2.35 |
12.00a |
0.00b |
<0.01 |
Coliforms, MPN/100ml |
|||
5.33 |
|
1.1x106 |
|
2.35 |
|
4.6x105 |
|
Table 1. Effect of treating waste water of the model of biodigester followed fish pond
Pig head/ / m3 biodigester |
Pig head/100 m2 water surface |
From pig pen |
Biodigester |
Fish pond |
P |
Temperature, oC |
|||||
19.7 |
9.12 |
29.67a |
31.00b |
28.42b |
<0.01 |
4.5 |
5.4 |
29.33a |
31.33b |
28.50b |
<0.01 |
pH |
|||||
19.7 |
9.12 |
7.47a |
6.43b |
7.08b |
<0.01 |
4.5 |
5.4 |
7.23a |
6.60b |
7.05b |
<0.01 |
DO, mg/l |
|||||
19.7 |
9.12 |
0.00a |
0.00a |
3.43b |
<0.01 |
4.5 |
5.4 |
0.00a |
0.00a |
3.48b |
<0.01 |
BOD5, mg/l |
|||||
19.7 |
9.12 |
1172a |
327.20b |
28.67b |
<0.01 |
4.5 |
5.4 |
1156a |
96.00b |
24b |
<0.01 |
COD, mg/l |
|||||
19.7 |
9.12 |
2120a |
486.67b |
47.20b |
<0.01 |
4.5 |
5.4 |
2043a |
186.70b |
42.30b |
<0.01 |
SS, mg/l |
|||||
19.7 |
9.12 |
1833a |
473.33b |
48.33b |
<0.01 |
4.5 |
5.4 |
1750a |
180.00b |
43.00b |
<0.01 |
Total nitrogen, mg/l |
|||||
19.7 |
9.12 |
63.48a |
23.72b |
6.69b |
<0.01 |
4.5 |
5.4 |
56.25a |
11.29b |
4.632b |
<0.01 |
Total Phosporus, mg/l |
|||||
19.7 |
9.12 |
386.90a |
109.11b |
10.01b |
<0.01 |
4.5 |
5.4 |
439.10a |
91.34b |
5.96b |
<0.01 |
Parasites, egg/l |
|||||
19.7 |
9.12 |
9.00a |
0.00b |
0.00b |
<0.01 |
4.5 |
5.4 |
11.00a |
0.00b |
0.00b |
<0.01 |
Coliforms, MPN/100ml |
|||||
19.7 |
9.12 |
|
|
4.6x104 |
|
4.5 |
5.4 |
|
|
2.4x104 |
|