Workshop-seminar, 21-24 August 2006,  MEKARN-CelAgrid   Workshop on Forages for Pigs and Rabbits
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Citation of this paper

The use of different levels of effluent from plastic biodigester loaded with pig pen for mulberry (Morus alba) tree growth

Effect of level of effluent from plastic biodigesters loaded with pig manure on the growth of mulberry (Morus alba) trees

Chiv Phiny, Khieu Borin and Chhay Ty

Center for Livestock and Agriculture Development, UTA-Cambodia
POB 2423, Phnom Penh 3, Cambodia
Phiny_kh@yahoo.com
 

Abstract

An agronomy trial to evaluate the effect of level of effluent from plastic biodigesters loaded with pig manure on the growth of mulberry (Morus alba) trees was conducted for one year (25 August 2004 to 25 August 2005) during both the dry and rainy seasons in the ecological farm of CelAgrid-UTA Cambodia, which is located in Kandal village, near to Phnom Penh, the capital of Cambodia. The trial included six treatments with four replications, divided into 4 blocks according to Complete Randomized Block Design. The effluent application levels were 0, 100, 250, 400, 550 and 700kg N / ha / year. Effluent was applied every 7days. Mulberry foliage was harvested (cutting height 60 cm above ground level) after 3 months and again at 2 month intervals. The foliage was separated into stem and leaf + petiole and analyzed for dry matter (DM) and nitrogen (N).

Dry matter biomass yield of mulberry foliage, and crude protein content of leaves increased linearly with the amount of effluent N applied.

Key words: Biodigester, effluent, manure, mulberry, biomass, fertilizer


Introduction

Mulberry is a traditional feed for silk worms and is reported to have a high edible biomass yield of 12 to 15 tonnes DM/ha/year, with a cutting interval of about 9 to10 weeks. The leaves have a high protein content (18 to 25% CP in DM) and high in vivo DM digestibility (75 to 85%). It thus has a high potential as a protein-rich forage supplement for ruminant production (Nguyen Xuan Ba et al. 2004). Mulberry plants grow very well in the rainy season, especially when fertilizer is applied. However, fertilizer use for mulberry production is very low in Cambodia because of the high cost of chemical fertilizer. Biodigester effluent is one option to be investigated in order to develop better crop growing practices. The advantages of passing manure through a biodigester are many and include gas production for cooking, improved health through elimination of pathogens and no loss of plant nutrients in the process (Bui Xuan An et al 1997).

A study was therefore carried out to compare the effect of different levels of effluent from a plastic biodigester charged with pig manure on biomass yield and composition of mulberry foliage. The objective of the trial was to determine the optimum level of effluent from a low-cost plastic biodigester with respect to the yield and composition of mulberry foliage.


Materials and methods

Location

The research was carried out at the ecological farm of CelAgrid-UTA Cambodia, located in Kandal village, Ro Lous commune, Khandal Steung district, Khandal Province. The center is about 25 km from Phnom Penh City. Previously the field had been used for monoculture rice production.

Experimental period

Soil and plot preparation, and preparation and transplanting of the mulberry seedlings was carried out from March to July 2004. The agronomy trial lasted from 25 August 2004 to 25 August 2005.

Plot size

Twenty four plots were prepared with a total area of 918 m2. Each plot had an area of 38.25 m2 (8.5m x 4.5m) and there were153 seedlings per plot (see Photo 1 and 2).

 

 

Photo 1: Plot preparation before transplantation

   Photo 2: Mulberry trees 2 months after transplanting

 

Design and treatments

Six (6) levels of effluent (0, 100, 250, 400, 550 and 700 kg of N/ha per year) were used in a production function design, with application rates made according the N content of the effluent from a low cost plastic biodigester linked to a pig pen. The 6 treatments had 4 replications divided into 4 blocks according to a Complete Randomized Block Design (Table 1). Planting distances of the cuttings were 60 cm and 50 cm between plants and rows, respectively.

The treatments consisted of six levels of fertilizer application with effluent from two low cost plastic biodigesters charged with pig manure:

 

 

Table 1: Layout of experimental mulberry plots

Block

 

                             Treatments

 

 

I

EFF550

EFF400

EFF100

EFF0

EFF700

EFF250

II

EFF400

EFF100

EFF0

EFF700

EFF250

EFF550

III

EFF100

EFF0

EFF700

EFF250

EFF550

EFF400

IV

EFF0

EFF700

EFF250

EFF550

EFF400

EFF100

The biodigesters

Two plastic biodigesters were constructed. The diameter of the plastic polyethylene tube was 100 cm and the length 10 m. Each biodigester was linked with pig pens. The total volume of each biodigester was 7 860 litres with the  liquid phase occupying 5 890 litres. Each biodigester discharged into an effluent tank of approximately 1 000 litres capacity.  Pig manure was put into the biodigesters through washing the pens 2 times per day.

Fertilizer application

During the dry season (December through May) the plots were irrigated by water pumped from underground sources . Effluent was pumped from the effluent tank and stored in 6 earthenware jars (about 500 litres capacity) close to the mulberry plots (Photo 3, 4) and was applied at weekly intervals in amounts adjusted according to the results of the N analysis .

 

 

 

Photo 3: Storage container for the effluent

   Photo 4: Applying the effluent
Harvesting

The mulberry plants were harvested by cutting the entire plant at 60 cm above soil level. The first time of harvesting was  4 months after planting, and subsequently at 2 month intervals. During harvesting, the biomass of mulberry foliage of each treatment was weighed and then separated into leaves and stems. The harvesting period lasted about 3 days.

Data collection

Samples of soil were taken from each plot before planting and after each harvest. Samples of effluent were analyzed for N before application to the mulberry plots. Before determining biomass yield, the proportions of leaves, stems and petioles were measured and samples from all treatments taken for analysis.

Measurements

The entire harvested plant (stems, petioles and leaves) was weighed after each harvest. DM was determined by using a microwave oven (Undersander et al 1993). The ratio of leaf and petiole to stem was calculated and approximately 100g of each plant fraction (stem, leaf and petiole) for each treatment was retained for analysis. Samples from replicates were analyzed for N and Ash (AOAC 1990) and also for water soluble dry matter (WVDM) and water soluble nitrogen (WVN). In each treatment and replicate plot a soil sample of 0.5 kg was taken at approximately 30cm depth and was kept for analysis of pH, N, DM and Ash.

Statistical analysis

The data were analyzed using the General Linear Model option of Minitab (version 13.31) ANOVA software. The sources of variation were level of effluent, harvest (1st, 2nd, 3rd, 4th and 5th) and error.


Results and discussion

Composition of effluent

Data on the composition of the biodigester effluent (Table 2) are similar to those reported by Bui Phan Thu Hang (2003).

Table 2: Composition of biodigester effluent from pig manure

 Parameter

Mean value

pH

6.59

DM, %

3.52

N, mg/litre

430

NH3-N, mg/litre

392

Effect of effluent on biomass yield and composition of mulberry leaves

Mean values for biomass yields of mulberry foliage in fresh and dry matter for individual treatments are given in Table 3 and 4. Main effects are compared in Table 5 and 6 and illustrated graphically in Figures 1, 2, 3 and 4.

Table 3: Effect of different levels of effluent application on the biomass yield of fresh mulberry foliage 

 

Treatment

0

100

250

400

550

700

SE

P

kg/plot

 

 

 

 

 

 

 

 

Whole plant

9.67

16.4

18.4

22.7

25.9

29.3

2.84

0.000

Leaf

6.36

10.1

11.9

14.4

16.5

18.6

1.95

0.000

Stem

3.31

6.32

6.58

8.28

9.38

10.8

1.10

0.002

kg/m2

 

 

 

 

 

 

 

 

Whole plant

0.25

0.43

0.48

0.59

0.68

0.77

0.07

0.000

Leaf

0.17

0.26

0.31

0.38

0.43

0.49

0.05

0.000

Stem

0.09

0.17

0.17

0.22

0.25

0.28

0.03

0.002

Tonnes/ha

 

 

 

 

 

 

 

 

Whole plant

2.53

4.29

4.82

5.93

6.76

7.67

0.74

0.000

Leaf

1.66

2.64

3.10

3.76

4.31

4.86

0.51

0.000

Stem

0.87

1.65

1.72

2.17

2.45

2.81

0.29

0.002

 

Table 4: Effect of level of effluent on biomass yield  (DM) of mulberry foliage 

Treatment

0

100

250

400

550

700

SE

P

kg/plot

 

 

 

 

 

 

 

 

Whole plant

3.6

5.8

6.3

7.7

8.5

9.0

0.86

0.000

Leaf

2.0

2.9

3.5

4.2

4.5

4.9

0.48

0.000

Stem

1.4

2.7

2.7

3.2

3.6

3.8

0.43

0.002

kg/m2

 

 

 

 

 

 

 

 

Whole plant

0.09

0.15

0.17

0.20

0.22

0.23

0.02

0.000

Leaf

0.05

0.08

0.09

0.11

0.12

0.13

0.01

0.000

Stem

0.04

0.07

0.07

0.08

0.09

0.10

0.01

0.002

Tonnes/ha

 

 

 

 

 

 

 

 

Whole plant

0.89

1.47

1.60

1.93

2.11

2.27

0.21

0.000

Leaf

0.51

0.77

0.90

1.09

1.17

1.27

0.12

0.000

Stem

0.38

0.70

0.70

0.84

0.94

1.00

0.11

0.002

Effects of biodigester effluent on the chemical composition of mulberry foliage are shown in Table 6.

 

 

Table 5: Effect of level of effluent on biomass yield  (DM) of mulberry foliage 

Treatment

0

100

250

400

550

700

SE

P

kg/plot

 

 

 

 

 

 

 

 

Whole plant

3.6

5.8

6.3

7.7

8.5

9.0

0.86

0.000

Leaf

2.0

2.9

3.5

4.2

4.5

4.9

0.48

0.000

Stem

1.4

2.7

2.7

3.2

3.6

3.8

0.43

0.002

kg/m2

 

 

 

 

 

 

 

 

Whole plant

0.09

0.15

0.17

0.20

0.22

0.23

0.02

0.000

Leaf

0.05

0.08

0.09

0.11

0.12

0.13

0.01

0.000

Stem

0.04

0.07

0.07

0.08

0.09

0.10

0.01

0.002

Tonnes/ha

 

 

 

 

 

 

 

 

Whole plant

0.89

1.47

1.60

1.93

2.11

2.27

0.21

0.000

Leaf

0.51

0.77

0.90

1.09

1.17

1.27

0.12

0.000

Stem

0.38

0.70

0.70

0.84

0.94

1.00

0.11

0.002

 

Biomass yields of the whole plant and the component leaves and stems increased linearly with level of effluent N (Figure 1).


Figure 1: Biomass yield response to fertilizer effluent

Crude protein increased in the leaves, but was unchanged in the stems, in response to effluent N application (Table 6 and Figure 2). Conversely DM content increased in stems but was unchanged in leaves in response to effluent N (Figure 3).

Table 6: Effect of level of effluent on the composition of mulberry foliage

 

0

100

250

400

550

700

SE

Prob

DM,%

 

 

 

 

 

 

 

 

Whole plant

37.1

35.7

34.5

34.8

32.8

31.1

0.53

0.000

Leaf

30.6

29.4

29.1

30.1

27.4

27.3

0.48

0.000

Stem

43.5

42.0

39.9

39.5

38.2

34.9

1.00

0.000

Crude protein, % in DM

Whole plant

10.8

12.1

11.9

12.4

11.6

12.7

0.57

0.216

Leaf

16.5

18.7

18.2

20.1

18.9

20.9

0.75

0.002

Stem

7.50

8.73

9.69

8.34

7.81

8.65

0.58

0.127

 

Figure 2: Trends in crude protein of leaves and stems in response to fertilizer effluent

  Figure 3: Trends in DM of leaves and stems in response to fertilizer effluent

The trends  for total biomass yield are similar to those of Ramos et al (Web page; no date) who applied swine lagoon effluent to mulberry plants, although the actual yields were much lower inour study.  Biodigester effluent from pig manure thus has been shown to be an effective nutrient source and can replace commercial fertilizer. Goat manure applied to mulberry in Costa Rica increased DM yield linearly (Benavides et al 1994) and yield was higher when N was applied in the form of manure in comparison with fertilizer (Takahashi and Kronka 1968).

The crude protein contents of mulberry leaves was significantly different among treatments (P<0.01), and ranged from16.5 % (EFF0) to 20.9 % (EFF700) of DM, values that are higher than those (15.0 - 15.3 %CP, DM basis) reported by Singh and Makar (2000). The positive effect of fertilizer level on the CP content in mulberry leaves was confirmed by Rodríguez et al (1994).


Conclusions


Acknowledgments

The authors would like to express their gratitude to the personnel of the Center for Livestock and Agriculture Development, UTA-Cambodia, for help with the experiment. Thanks for financial support by the Cambodian Agricultural Research Fund (CARF) to CelAgrid which made it possible for us to carry out this research. Thanks are given to Dr.John Schiller, consultant of the CARF project, and to Dr. John Skeritt, Deputy Director General - Research, Australian Centre for International Agricultural Research (ACIAR), for assisting in the financial management, and providing an internship.


References

AOAC 1990: Official methods of chemical Analysis. Association of Official Agricultural Chemists. Washington DC (16th edition)

Benavides J, Lachaux M y Fuentes M 1994: Efecto de la aplicación de estiércol de cabra en el suelo sobre la calidad y producción de biomasa de morera (Morus sp.). In Benavides, J.E. Árboles y arbustos forrajeros en América Central. CATIE, Turrialba, Costa Rica. 2: 495-514

Bui Phan Thu Hang 2003: Effect of dimensions of plastic biodigester (width:length ratio) on gas production and composition of effluent;  RetrievedOctober 31, 106, from MEKARN Mini-projects. http://www.mekarn.org/msc2003-05/miniprojects/webpage/hangctu.htm

Bui Xuan An, Preston T R and Dolberg F 1997: The introduction of low-cost polyethylene tube biodigesters on small scale farms in Vietnam. Livestock Research for Rural Development (9) 2:27-35 http://www.cipav.org.co/lrrd/lrrd9/2/an92.htm

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Singh B and Makkar H P S 2000: The potential of mulberry foliage as feed supplement in India.FAO Animal Production and Health Paper 147, p. 139-156.  http://www.iaea.org/programmes/nafa/d3/public/mulberry-fullpaper.pdf

Takahashi R and Kronka R N 1986: Efeitos dos diferentes tipos de adubacao na producao de amoanim. Nova Odessa 46: 157-164

Undersander D, Mertens D R and Theix N 1993: Forage analysis procedures. National Forage Testing Association. Omaha pp 154

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