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V. FORAGE AND FODDER RESOURCES
Backer and Bakhuizen van den Brink
(1963) showed that there are about 238 plant families with about 952 genera and 1 047
species in Java and Madura. In the small island of Bali there are 50 genera of grasses and
ground legumes and 55 species of fodder shrubs and trees used as ruminant feed (Nitis et
al., 1980).
Agroforestry, which has existed in
Indonesia for 100 years and has evolved through trial and error, is not only a way of
increasing the timber, energy, feed and food production, but also contributes to
conservation of the environment. Depending on the dominant and specific production of its
components, agroforestry can be specified into many variants (Nitis, 1997). The transition
leading to dominance of either the silvicultural system, pastoral system, or
agrosilvopasral system depends on ecological and socioeconomic conditions. During the land
reforms of 1963 many forests were cleared for smallholder farming and many grasslands
converted into semi-intensive farming, thus increasing the planting of shrubs and trees
for livestock feed. Grain, pulses and tubers are the main food crops. Wild grass and
legumes in food crops are considered weeds. After harvest, the field is either bare or
invaded by volunteer herbaceous species. No land is specially allocated to grow forage.
Grass, legumes, shrubs and trees are grown on the bunds, on sloping land along terraces
and on field boundaries.
Grasses and legumes growing wild under
plantation crops are thought weeds and are cleared periodically. Leguminous trees and
shrubs, on the other hand, are grown as supports for vanilla, shade for coffee, or green
manure for the crop. They are also grown along plantation edges and lopped periodically to
prevent shading.
Based on its leaf canopy, the forest can
be classified into evergreen and deciduous forests. Because light intensity becomes the
first-limiting factor, forage growing under forest is shade-tolerant. In the mixed
deciduous forest, the main undergrowth consists of Bambusa, Imperata, Eulalia,
Casearia, Euphorbia, Acroceras, Morinda, Acacia, Poecia, Leersia and Eupatorium
species. In abandoned swidden, the plants are Eulalia, Leersia, Sida, Solanum,
Thysanolaena, Acroceras, Ageratum and, Bambusa. In the dry season no green forage is
left, because the forest floor is covered with dried leaves, shoots and pods.
In the dry-land farming area, farmers
crop the land continuously for three years then leave it fallow for four to six years.
During the fallow grasses and herbs colonise the field. This fallow is used to tether
cattle and goats; tethered grazing is usually very intense, so no forage is left for the
dry season.
Forage and fodder in natural
grassland
Natural grassland develops as a result of
shifting cultivation and the degradation of climax forest (Deptan, 1988) and is maintained
by overgrazing and uncontrolled burning. Large areas of grassland are found is Sumatra,
Kalimantan, Sulawesi, Nusa Tenggara, and Irian Jaya (Ivory and Siregar, 1984). The pasture
consists of many grasses and legumes, with the commonest genera being Imperata,
Paspalum, Chloris, Eleusine, Themeda, Tetrapogon, Polytrias, and Desmodium.
During the dry season the land is almost bare, because of overgrazing and uncontrolled
burning. Imperata cylindrica occupies 16 000 km2 and is increasing by 1
500 km2 annually (Surjani, 1970).
Critical land is that which is no longer
capable of playing a role in production, hydrology, or ecology (Deptan, 1988). It develops
as a result of overgrazing, continuous cultivation, bush-fires, and deforestation of
marginal land. Forage in such areas is dominated by annuals, which grow quickly and
produce plenty of seeds during the wet season but withers in the dry season. Shrubs and
trees, grow well during the wet season but become stunted during the dry season.
Table 3. Native pasture yield
(tonnes/dry matter/ha) during wet season in Bali 1)
| Agroecology |
Climatic zone |
Mean |
| |
B |
C |
D |
E |
F |
|
| Topography
: |
| Lowland |
* |
1.55 |
1.02 |
1.37 |
1.82 |
1.44 +0.34 |
| Hill |
0.92 |
0.76 |
1.04 |
1.25 |
3.27 |
1.45 +1.04 |
| Upland |
1.31 |
2.10 |
0.68 |
0.33 |
1.91 |
1.27 +0.77 |
| Land
utilization: |
| Wetland |
2.03 |
0.97 |
1.71 |
0.48 |
2.89 |
1.61 +0.94 |
| Dry-land |
1.06 |
1.23 |
1.16 |
0.91 |
1.85 |
1.24 +0.36 |
| Plantation |
0.82 |
1.04 |
0.95 |
1.02 |
1.59 |
1.09 +0.29 |
| Soil
condition : |
| Wet |
1.88 |
1.07 |
1.43 |
0.54 |
1.81 |
1.36 +0.55 |
| Dry |
0.79 |
1.28 |
1.26 |
1.39 |
1.18 |
1.18 +0.23 |
| Mean |
1.26+0.51 |
1.25+0.42 |
1.16+0.32 |
0.91+0.42 |
2.04+0.69 |
|
1)Nitis et al.
(1980). * Not in lowlands.
Forage and fodder yields
Botanical composition is affected by season
and land utilization (Nitis et al., 1980). In the wet season, the wet land,
dry-land, and plantation areas are dominated by genera of Axonopus, Chrysopogon and
Sehima, respectively; in the dry season crop land is dominated by genera of Paspalum.
Yield of native pasture is affected by season, by climatic zone, topography, land
utilization and soil conditions. In the wet season the highest pasture yield is in
climatic zone F in the hills (Table 3); in the dry season the highest yield is in climatic
zone E in the uplands (Table 4). Lopping yield (amount lopped to be fed to ruminants) of
43 species of fodder shrubs and trees in the wet season varied from 0.10 20.23 kg
DM per tree; in the dry season the yield of 55 species varied from 0.13 23.24 kg DM
per tree. In the wet season the highest yield of shrub and tree fodder is in climatic zone
E in coastal area (Table 5); while in the dry season the highest yield is in climatic zone
E in dry-land area (Table 6).
Table 4. Native pasture yield (tonnes
DM/ha) during dry season in Bali province1)
| Agroecology |
Climatic zone |
Mean |
| |
B |
C |
D |
E |
F |
|
| Topography
: |
| Lowland |
* |
0.92 |
1.29 |
1.37 |
0.80 |
1.09+ 0.28 |
| Hill |
0.74 |
1.13. |
0.79 |
1.39 |
1.86 |
1.18 +0.46 |
| Upland |
1.86 |
1.24 |
0.37 |
3.54 |
1.30 |
1.46 + 1.21 |
| Land
utilization: |
| Wetland |
1.09 |
0.86 |
1.05 |
1.19 |
1.21 |
1.08 + 0.14 |
| Dry-land |
0.98 |
1.38 |
0.89 |
1.02 |
1.26 |
1.11 + 0.21 |
| Plantation |
0.93 |
0.92 |
1.21 |
1.15 |
1.01 |
1.04 + 0.13 |
| Soil
condition : |
| Wet |
0.95 |
1.48 |
1.46 |
1.24 |
0.90 |
1.21 + 0.28 |
| Dry |
1.11. |
1.40 |
0.85 |
1.85 |
1.01 |
1.24 + 0.39 |
| Mean |
0.95+0.13 |
1.17+0.25 |
0.99+0.34 |
1.59+0.82 |
1.14+0.33 |
|
1)Nitis et al.
(1980). * Not in lowland area.
Table 5. Shrub and tree leaf yields
(kg DM/tree) during the wet season in Bali1)
| Agroecology |
Climatic zone |
Mean |
| |
B |
C |
D |
E |
F |
|
| Topography
: |
| Lowland |
* |
0.56 |
4.11 |
6.95 |
7.50 |
4.78 + 3.18 |
| Hill |
1.92 |
1.00 |
2.72 |
3.72 |
5.11 |
2.89 + 1.59 |
| Upland |
2.09 |
3.60 |
1.87 |
1.39 |
4.73 |
2.54 + 1.67 |
| Land
utilization : |
| Wetland |
2.45 |
2.19 |
3.22 |
3.54 |
3.80 |
3.04 + 0.69 |
| Dry-land |
2.41 |
1.65 |
3.05 |
6.32 |
5.83 |
3.85 + 2.09 |
| Plantation |
4.11 |
5.73 |
2.98 |
3.83 |
4.07 |
4.14 + 0.99 |
| Soil
condition : |
| Wet |
3.86 |
3.25 |
2.49 |
3.21 |
3.49 |
3.26 + 0.50 |
| Dry |
2.18 |
1.25 |
0.98 |
4.42 |
5.01 |
2.77 + 1.84 |
| Mean |
2.72+ 0.89 |
2.40+ 1.71 |
2.68+ 0.94 |
4.05+ 2.01 |
4.94+ 1.29 |
|
1)Nitis et al.
(1980). * Not in lowland area.
Forage and fodder quality
In the wet season, native pasture contains
more crude protein (CP), major minerals K and Mg and trace minerals Zn and Mo than that in
the dry season (Table 7). In the dry season the highest CP content is in native pasture in
climatic zone C in the hills (Table 8). In the wet season shrub leaves contained less CP
than during the dry season; while the reverse is true for tree leaves (Table 8). The
highest CP content of the shrub leaves during both seasons is from the legumes Leucaena
leucocephala and Gliricidia sepium,; while the highest CP content of the tree
leaves during the wet and dry seasons is from the legumes Wrightia calveina and Erythrina
lithosperma, respectively. For Gliricidia sepium the highest CP content is in
the wet land farming area; while for the Erythrina variegata the highest CP content
is climatic zone B, (Table 10).
Table 6. Shrub and tree leaf yields
(kg DM/tree) during the dry season in Bali1)
| Agroecology |
Climatic zone |
Mean |
|
B |
C |
D |
E |
F |
|
| Topography : |
| Lowland |
* |
4.96 |
4.15 |
4.18 |
6.33 |
4.91 + 1.70 |
| Hill |
1.23 |
4.08 |
5.01 |
4.52 |
4.98 |
3.96 + 1.58 |
| Upland |
2.79 |
3.20 |
3.94 |
1.98 |
4.27 |
3.24 + 0.91 |
| Land utilization : |
| Wetland |
2.23 |
6.94 |
3.97 |
4.76 |
4.11 |
4.40 + 1.70 |
| Dry-land |
2.55 |
4.89 |
3.36 |
8.35 |
3.39 |
4.51 + 2.31 |
| Plantation |
2.79 |
3.06 |
3.76 |
6.24 |
3.19 |
3.81 + 1.40 |
| Soil condition : |
| Wet |
3.22 |
2.38 |
5.26 |
1.29 |
3.73 |
3.18 + 1.49 |
| Dry |
1.96 |
2.22 |
5.39 |
4.71 |
4.48 |
3.75 + 1.56 |
| Mean |
2.40+ 0.66 |
3.97+ 1.59 |
4.36+ 0.76 |
4.50+ 2.23 |
4.31+ 1.00 |
|
1)Nitis et al.
(1980). * Not in lowland area.
Table 7. Proximate and mineral
compositions of native pasture in Bali1)
| Composition |
Wet season2) |
Dry season2) |
| |
Range |
Average |
Range |
Average |
| Proximate
(%) : |
|
|
|
|
| Crude
protein (CP) |
7.73 18.24 |
12.99 |
5.42-17.70 |
11.56 |
| Crude fibre
(CF) |
21.30 27.26 |
24.28 |
23.03-34.40 |
28.72 |
| Major
mineral (%) : |
|
|
|
|
| Potassium
(K) |
2.04 - 4.81 |
3.43 |
1.85 3.31 |
2.58 |
| Magnesium
(Mg) |
0.12 - 0.53 |
0.33 |
0.10 0.41 |
0.26 |
| Trace
mineral (ppm) : |
|
|
|
|
| Zinc (Zn) |
50.7 116.6 |
83.70 |
19.60-51.8 |
35.70 |
| Molybdenum
(Mo) |
0.35 - 2.36 |
13.55 |
0.87- 3.61 |
2.24 |
| |
|
|
|
|
1) Nitis et al,
1985. 2) From 15 species.
Table 8. Crude protein content (% DM)
of native pasture in the dry season in Bali1)
| Agroecology |
Climatic zone |
Mean |
| |
B |
C |
D |
E |
F |
|
| Topography
: |
| Lowland |
* |
8.43 |
7.10 |
8.98 |
9.32 |
8.46+ 0.98 |
| Hill |
12.52 |
9.38 |
10.76 |
9.16 |
3.73 |
9.11 + 3.29 |
| Upland |
12.95 |
13.62 |
11.20 |
9.00 |
4.62 |
10.28+ 3.63 |
| Land
utilization: |
| Wetland |
12.99 |
13.31 |
9.36 |
9.64 |
9.80 |
11.02+1.95 |
| Dry-land |
12.72 |
10.85 |
9.83 |
10.70 |
5.03 |
9.83 + 2.88 |
| Plantation |
12.72 |
12.41 |
11.15 |
7.21 |
4.49 |
9.60 + 3.60 |
| Soil
condition : |
| Wet |
9.94 |
10.52 |
7.56 |
11.63 |
11.68 |
10.27+ 1.68 |
| Dry |
10.01 |
10.63 |
12.10 |
8.55 |
4.64 |
9.19 + 2.84 |
| Mean |
11.98+1.38 |
11.14+1.84 |
9.88+ 1.79 |
9.36+ 1.34 |
6.66+ 3.08 |
9.75 + 2.64 |
1)Nitis et al. (1980). *
Not in lowland area.
Deleterious compounds found in forages
and fodder are: cyanoglucosides, fluoroacetic acid, tannin, prussic acid, mimosine, latex
and oxalic acid (Table 10). Some fodders such as Bauhinia variegata may cause
decrease in milk yield, Bridella retusa may cause dysphagia, Albizia stipulata
may cause haematuria, Ficus hispida may cause abortion and Schima
wallichii may cause hair loss and skin disease (Table 11). Ways to overcome the
anti-nutritive factors include supplementation, dilution, simple treatment, and rumen
microbial activity (Lowry, 1989). Mimosine in Leucaena can be toxic to some
ruminants if there is no 3,4 DHP detoxifying bacteria in their rumens (Jones,
1986); ruminants can be inoculated or put in contact with resistant ruminants (Munoz and
Seifert, 1991).
Table 9. Proximate composition
of shrubs and tree fodders in Bali1)
| Plant |
Nutrient (%) |
Wet season |
Dry season |
| |
|
Range |
Average |
Range |
Average |
| Shrub leaf 2) |
CP |
10.80-32.42 |
21.76 |
13.17-35.92 |
24.55 |
| |
CF |
9.77-24.44 |
17.11 |
14.42-35.69 |
25.06 |
| |
Ash |
6.7226.55 |
16.64 |
5.07-24.27 |
14.67 |
| |
TDN |
31.11-88.91 |
60.01 |
5.24-90.08 |
47.66 |
| Tree leaf3) |
CP |
9.67 33.32 |
21.49 |
8.30-31.35 |
19.83 |
| |
CF |
7.34 31.02 |
19.18 |
10.79-36.36 |
23.58 |
| |
Ash |
6.21 27.35 |
16.78 |
5.43-24.18 |
14.81 |
| |
TDN |
20.45 76.18 |
48.32 |
10.28-64.27 |
37.28 |
1) Nitis et al., (1985).
2) 13 spp in wet season and 14 spp in dry season. 3)30 spp in wet season and 41 spp in dry
season.
Utilization of forage and fodder
Roughage fed to ruminants consists of
wild herbage, fodder and crop residues. Fodder is shrub and tree leaves and crop residues
are straw and stover(Nitis, 1998). In Bali goats are fed more shrub and tree leaves than
cattle, while buffalo are fed little (Table 12). Rice straw, corn stover and banana
pseudostems are not fed to goats, but cassava tops are fed when available. Cattle in the
dry-land farming are fed more leaves than those in plantations and rice areas (Table 13);
in the rice areas they are fed straw; in dry-land farming and plantation areas they are
fed maize stover and cassava tops.
Limitations to forage and fodder
production
No land is allocated to grow livestock
feed in smallholder farming area, so forage and fodder are grown on bunds, around fences,
fallow and land not suitable for crops. In some places farmers have other priorities than
fodder for plants. Ficus benjamina is a holy tree so it is not lopped. Imperata
cylindrica is used for thatching special houses, so that it is only tether-grazed
during very early regrowth after harvesting every two years. Artocarpus integra is
not lopped regularly, otherwise it does not fruit. Coconut fronds are not commonly fed to
livestock since the young leaf is used as accessory in ceremonies, the old fronds are used
as firewood.
Pests cause little damage on
properly managed forage and fodder. However a psyllid (Heteropsylla cubana)
outbreak was reported in Hawaii in 1984 and in the Asia and Pacific regions in 1985 (NFTA,
1989). In seriously infested areas in Indonesia, control measures using resistant Leucaena
varieties, effective predators, insecticides and management have had varying degrees of
success. In some areas Gliricidia is infested with an aphid (Aphis craccivora)
particularly at the onset of the rains, which causes blackening of the leaf surface and in
severe cases the death of the leaf primordia and shedding of young leaves (Nitis et al.
1989). The aphid exudate causes yellowing and even death of the Cenchrus ciliaris
grown with Gliricidia. Evaluation of the 16 provenances of Gliricidia sepium
showed that 3 provenances (G14, G17 and N14) are quite resistant to aphid infestation
(Nitis et al., 1991).
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