Forages in Oil
Palm and Rubber Plantations in Malaysia
Hassan A. Wahab
Malaysian Agricultural Research and Development Institute (MARDI)
P.O. Box 62, 26700 Muadzam, Shah, Pahang, Malaysia
ABSTRACT
The forage resources under plantations in Malaysia
was described with regards to the factors affecting them, their quality,
availability and their utilization for livestock production. Forages
under plantation crops consist of native grasses, legumes, broadleaf
species and ferns, most of which are palatable to animals. The botanical
composition, yield and quality of these species are influenced by interacting
factors of light, moisture and age of trees or plantation crop and kind
of livestock raised. Sheep however, was found most suited to be integrated
with rubber.
INTRODUCTION
Oil palm and rubber are the major plantation
crops in Malaysia. They cover an estimated area of over 4 million hectares. The inter
row areas of these crops are usually covered with vegetation comprising
of leguminous cover crops, grasses, broadleaf species and ferns which
form a naturalized pasture and can be utilized as forages for livestock
production. This feed resource was estimated to comprise as much as 83%
of the total forage resource available in the country (Devendra 1981).
It is one of the most extensive and underutilized forage resources in
Malaysia.
There are about 60 to 70 plant species growing under the
young plantation crops and the number decline to 20 to 30 species under
older trees. Out of these, only about 70% of these species are palatable
and can contribute as forage for livestock production (Chen et al.
1978; Wan Mohammad 1977; Hassan and Abdullah 1991).
This paper discusses the forages resources
that are available in oil palm and rubber plantations in terms of the
species, botanical composition, quality, quantity as well as the utilization
of these forages as animal feed and the impact to the livestock and oil
palm/rubber industries in Malaysia.
Factors affecting forage resources under plantations
Forages under plantation crops consist of native grasses, legumes,
broadleaf species and ferns, most of which are palatable or grazed by
the animals. If legume cover crops are sown at the time of planting of
oil palm or rubber, these legumes usually dominate the native species
in the inter rows for the first three to five years. These legume cover
crops are grown in combinations of Calopogonium mucunoides,
C. caeruleum, Centrosema pubescens and Pueraria phaseoloides.
They are planted for soil erosion control during the first 8-10 months
of land clearing. The species, botanical composition, yield and quality
of these forages are constantly changing because of the influence of many
interacting factors such as light and moisture.
Light is the most critical factor in determining the type
of forage species available and in determining the growth of the forage.
In the plantations, the amount of photosynthetically active radiation
(PAR) that reaches the ground vegetation is proportionally reduced as
it passes through the canopy of the trees. The amount of light reaching
the undergrowth varies with age, height, spacing and canopy characteristics
of the tree crops. Generally the amount of PAR declines with increasing
age of the trees (Figure 1).
In rubber and oil palm, the percentage of light under
the tree canopies drops to below 20% of full sunlight at the tree age
of 6 to 7 years and this amount changes only slightly thereafter. The
percentage of light increases significantly after the trees are 15 to
20 years old when the canopies open up slightly.
|
Figure 1. Light transmission
(%) profiles in relation to age of oil palm and rubber
(Source: Wilson and Ludlow 1990) |
It must be realized that under reduced light, that presence
of the dry matter production of the native species is
low. These species are adapted to the environment through morphological
adaptations. Wong (1991) showed that shading significantly reduced tiller
production, stem stubble and roots but increased the specific leaf area
(leaf area per unit leaf weight), shoot:root ratio and leaf:stem ratio.
In Malaysia, the rainfall is high (>2000 mm per year)
but is not evenly distributed. Thus, agro-ecological zones based on rainfall
distribution have been recognized. Generally there is little competition
for moisture between the tree crops and the native forages, except when
there is a prolonged dry spell.
The air temperature under tree crops is generally lower
than in the open. Chen (1989) showed that air temperature under rubber
was lower than in the open throughout the day with a maximum of 2 to 3°C
during the afternoon. Soil temperature also showed the same trend with
1to 2°C lower in the shade at 5 cm depth compared with open pastures (Chen
et al. 1991). In general, the decrease in air and soil temperature is
too small to have any influence on native pasture growth under tropical
environment (Wilson and Ludlow 1991).
Forage species
Forage species that grow in oil palm and rubber plantations include all
the palatable plant species that thrive under this microenvironment.
Generally, the leguminous cover crops comprising of Pueraria phaseoloides,
Calopogonium mucunoides, Calopogonium caeruleum and Centrosema pubescens
dominate the ground vegetation in the early stages of the tree crop development
(first 5 years) and they are gradually replaced by the shade-tolerant
species when the canopies close. These shade-tolerant species persist
for almost two-third of the economic life span of the tree crops (Ahmad
Tajuddin and Wan Zahari 1991).
Species richness under oil palm and rubber has been highlighted
and recognized. Species of grasses, broadleaves, legumes and ferns that
are commonly found growing under oil palm and rubber in Malaysia are shown in Table 1. These
species have been grouped into palatable and non-palatable species and
only those palatable species contribute to the forage resource available
under plantation crops.
Palatable species are those that are ‘accepted’ or grazed
by cattle and sheep.
| Table 1. Palatable
and non-palatable plant species commonly found in oil palm and rubber
plantations. |
| PALATABLE
SPECIES |
NON-PALATABLE SPECIES |
| Grasses
Axonopus compressus
Brachiaria mutica
Chrysopogon aciculatus
Cyrtococcum oxyphyllum
Digitaria ascendens
Eleusine indica
Imperata cylindrica
Ischaemum muticum
Ottochloa nodosa
Panicum repens
Paspalum conjugatum
Broadleaves
Asystasia intrusa
Cleome rutidosperma
Commelina nudiflora
Croton hirtus |
Hydrocotyl asiatica
Mikania cordata
Legumes
Calapogonium mucunoides
Centrosema pubescens
Desmodium ovalifolium
Desmodium triflorum
Mimosa pudica
Pueraria phaseoloides
Ferns
Lygodium flexuosum
Nephrolepis biserrata
Pteridium esculentum |
Grasses
Themeda arguens
Broadleaves
Ageratum conyzoides
Borreria latifolia
Eupatorium odoratum
Hyptis brevipes
Lantana camara
Melastoma malabathricum
Legumes
Calapogonium caeruleum
Cassia tora
Mimosa invisa
Ferns
Dicraopteris linearis
Stenochaena palustris |
|
|
|
With regards to ferns, the animals do not lavish on them
and they are normally grazed last after all the other palatable species
have been grazed.
The non-palatable broadleaf species are mainly woody shrubs
such as Melastoma, Clidemia, Eupatorium, Lantana
and Hedyotis. These species may comprise 10-30% of the
total dry matter of forage depending on age of the tree canopy (Wong and
Chin 1998).
Forage botanical composition
Under plantation crops, the botanical composition of the forage changes
as the trees become older. This is due to the declining amount of light
reaching the ground vegetation. As the trees grow and become older, the
canopies of the trees close up and the amount of light reaching the ground
is reduced. Only shade tolerant species are able to grow under this environment.
Under oil palm, grasses, legumes and broadleaf species dominated the native
forage in the first five years after planting. The legumes, mostly the
cover crops decline in their contribution to the forage after the fifth
year, once the oil palm canopy has closed up. The proportion of grasses
changes slightly but broadleaf species declined as the trees mature.
But ferns and non-edible broadleaf species which tolerate high shade increased
in their proportion with the increase in age of the oil palm (Table
2). Under rubber, the scenario is slightly different. The proportion
of grasses declined with increasing age of the rubber trees even though
the light penetration has increased slightly because the canopy has opened
up towards the end of the economic life of the rubber trees. The legumes
showed similar trend with that of grasses. Proportions of ferns and the
non-edible broadleaf species increased with increasing age of the rubber
trees.
Wong (1985, 1990) has screened forage grasses and legumes
under different shade levels and grouped forage species both native as
well as introduced into high, medium and low shade tolerance (Table
3).
Shade tolerance was defined as the relative growth performance
of plants in shade compared to that in full sunlight as influenced by
regular defoliation. It embodies the attributes of both dry matter productivity
and persistence of the species.
| Table 2. Botanical
composition (% dry matter) and forage dry matter available (kg/ha)
under different age groups of oil palm and rubber canopies |
| Age of palm /tree (years) |
3 |
5 |
10 |
15 |
20 |
25 |
30 |
| OIL PALM
Grasses
Legumes
Edible dicots
Ferns
Non-edible dicots
DM yield (kg/ha) |
39.76
28.65
22.54
0.16
8.78
2990 |
59.04
5.66
18.50
3.75
3.05
2164 |
55.64
0.50
13.00
23.60
7.2
475 |
52.46
0.40
8.08
19.41
19.65
825 |
37.80
5.55
5.59
26.86
24.20
467 |
26.25
2.22
17.69
37.79
17.05
343 |
31.20
-
8.44
32.50
27.85
998 |
| RUBBER
Grasses
Legumes
Edible dicots
Ferns
Non-edible dicots
DM yield (kg/ha) |
53.35
31.28
8.22
-
7.16
1869 |
52.12
15.97
8.93
18.21
4.77
435 |
59.99
2.07
2.52
31.33
4.06
542 |
21.82
6.32
4.94
62.27
4.65
520 |
19.18
4.26
1.00
58.00
17.55
628 |
13.57
1.43
3.66
63.18
18.16
1282 |
12.89
3.78
7.25
55.84
20.23
1975 |
Source: Chen et al. (1991)
| Table 3. Shade tolerance
of some tropical forage |
| Shade tolerance |
Grasses |
Legumes |
| High |
Axonopus compressus
Brachiaria miliiformis
Ischaemum aristatum
Ottochloa nodosa
Paspalum conjugatum
Stenotaphrum secundatum |
Calopogonium caeruleum
Desmodium hetrophyllum
Desmodium ovalifolium
Flemengia congesta |
| Medium |
Brachiaria bizantha
Brachiaria decumbens
Brachiaria humidicola
Digitaria setivalva
Imperata cylindrica
Panicum maximum
Pennisetum purpureum
Setaria sphacelata |
Calopogonium mucunoides
Centrosema pubescens
Desmodium triflorum
Pueraria phaseoloides
Desmodium intortum
Leucaena leucocephala |
| Low |
Brachiaria mutica
Cynodon plectostachyus
Digitaria decumbens
Digitaria pentzii |
Stylosanthes hamata
Stylosanthes guianensis
Zornia diphylla
Macroptilium atropurpureum |
Source: Wong (1990)
The forage species that tolerate high shade are those
native forage species commonly found growing under plantation crops.
Axonopus compressus, Ischaemum aristatum, Ottochloa
nodosa and Paspalum conjugatum are the major grass species
while Desmodium heterophyllum and D. ovalifolium are
the native legumes. Calopogonium caeruleum and Flemengia
congesta are not palatable to livestock.
The medium shade tolerant species are found in the plantation
in the first five years after planting of the plantation crops and they
decline thereafter because the tree canopies have close up and less light
can penetrate through to the ground. If one needs to plant forages in
the plantations, then these medium shade tolerant species are suitable
because they can provide high forage production up to five years before
light becomes limiting.
In terms of morphological adaptations of the plants to
shade, tiller production and leaf, stem, stubble and root productions
are often reduced at low light with formation of thinner leaves with higher
moisture content and higher specific leaf area (Wong et al.
1985a, b). Grasses with high shade tolerance were found to have a higher
specific leaf area and leaf area ratio than those with low shade tolerance.
Quality of native forage
Contrary to general belief that native forages are low in quality,
the nutritive values of grazed native pasture species under plantation
crops are high. The crude protein content of native grasses on offer
ranges from 6.7 to 11.4 % (Lane 1984; Chen et al. 1991). It
is quite common that the animals through selective grazing may consume
forages with 16% crude protein or even higher especially when grazing
broadleaves and legumes.
The estimated concentrations of metabolizable energy (ME)
are 7.1 to 8.9 MJ/kg dry matter (DM) for grasses on offer and up to 10.1
MJ/kg DM for forages consumed (Ahmad Tajuddin and Wan Zahari 1991).
Chen et al (1991) reported ME values of 7.13, 7.17, 5.34 and 8.34 MJ/kg
DM for grasses, legumes, ferns and edible broadleaves, respectively.
Table 4. Proximate
analysis of some of the palatable native forages under oil palm
and rubber. |
| Species |
DM
(%) |
CP
(%) |
CF
(%) |
EE
(%) |
P
(%) |
Ca
(%) |
Mg
(%) |
ME 1
MJ/kg) |
| Axonopus
compressus |
29.6 |
7.5 |
30.8 |
1.4 |
0.05 |
0.39 |
0.36 |
8.7 |
| Brachiaria
mutica |
27.5 |
6.3 |
32.4 |
1.8 |
0.08 |
0.14 |
0.04 |
8.2 |
| Imperata
cylindrica |
36.5 |
11.7 |
32.0 |
1.9 |
0.10 |
0.20 |
- |
9.2 |
| Ischaemum
muticum |
35.0 |
14.9 |
27.7 |
1.6 |
0.07 |
0.30 |
0.13 |
10.6 |
| Paspalum
conjugatum |
21.7 |
11.0 |
28.6 |
1.6 |
0.09 |
0.31 |
0.43 |
9.2 |
| Asystasia
intrusa |
12.1 |
19.0 |
25.6 |
3.3 |
0.31 |
0.50 |
0.50 |
11.7 |
| Mikania
cordata |
9.6 |
17.6 |
22.9 |
2.4 |
- |
- |
- |
11.3 |
| Calopogonium
mucunoides |
23.0 |
20.1 |
24.8 |
65.3* |
- |
- |
- |
- |
| Centrosema
pubescens |
24.3 |
22.2 |
30.9 |
62.7* |
- |
- |
- |
- |
| Pueraria
phaseoloides |
19.1 |
19.9 |
28.8 |
67.4* |
- |
- |
- |
- |
* TDN (%)
1 Metabolizable Energy (MJ/kg DM) = 13.3 + 0.17 (CP) – 0.19 (CF)
Adapted from Ahmad Tajuddin and Wan Zahari (1991) and Chin (1991)
The nutritive values of some common native pasture species
under plantation crops in Malaysia are shown in Table 4. Besides the
leguminous cover crops of C. mucunoides, C. pubescens
and P. phaseoloides, Assassin intrusa and Mikania
cordata have also high levels of crude protein. They are very palatable
and thus making them excellent forage species.
Even though native grasses have slightly lower crude protein
content (6 to 11%) for good animal growth requirement, the fact that they
exist in combinations with broadleaves such as Asystasia and
Mikania and with leguminous cover crops which contain high crude
proteins make them good forages. Rosli (1998) reported that a combination
of 60% Asystasia and 30% Paspalum can be considered
as good forage. In terms of animal nutritional requirements, Wong and
Chin (1998) showed that the edible forage resource at different ages
of the oil palm plantation are adequate to the grazing cattle in terms
of metabolizable energy and more than adequate for crude protein requirement
(Table 5).
| Table 5. The botanical
composition and estimated forage quality under different ages oil
palm |
| Age of oil palm (years) |
Botanical composition (%) |
Forage Quality |
| Grasses |
Dicot |
Legumes |
Ferns |
Mean
ME
(MJ/kg) |
Mean
Protein (%) |
Mean
Ca (%) |
Mean
P
(%) |
| 3-5 |
65 |
23 |
19 |
2 |
7.42 |
12.8 |
0.25 |
0.30 |
| 6-10 |
64 |
18 |
3 |
15 |
7.31 |
11.8 |
0.59 |
0.27 |
| ›10 |
50 |
13 |
2 |
35 |
6.87 |
12.2 |
0.63 |
0.23 |
Source: Wong and Chin (1998)
Table 6 shows the quality of native forages under plantations
as compared to the quality of guinea and legumes under legume-based pasture
and improved grasses under nitrogen fertilized pasture. Forages under
plantation were comparable to legume based pasture in terms of N content,
dry matter digestibility and metabolizable energy. However, quality of
native forages is slightly lower than that of N fertilized grasses.
| Production system |
N
(%) |
DMD
(%) |
ME
(MJ/kg DM) |
| a) Under Plantation
Grasses
Legumes
Ferns
Edible dicots
b) Legume-based pasture
Guinea
Legumes
Weeds
c) N-fertilized pasture
Digitaria setivalva
Guinea
Signal grass |
1.58
3.07
1.96
2.81
1.60
3.55
1.97
2.61
2.54
2.39 |
47.61
47.80
35.60
55.60
52.62
40.33
48.04
59.40
52.62
56.09 |
7.13
7.17
5.34
8.34
7.80
6.01
7.13
8.78
7.80
8.31 |
Source: Wong and Chin (1998)
AVAILABILITY OF FORAGES
Forage dry matter yield was strongly related to light
transmission through the canopy to the ground vegetation. Available forage
dry matter declines from over 5 tons/ha in young rubber and oil palm plantation
to below 1 ton/ha when the canopy closed (Chen and Othman 1983; Tajuddin
and Chong 1994). Similar trend was also obtainedby Chen and Harun (1994)
which they reported dry matter yield of 1230 kg/ha dry matter under 7
year old palm, while under 17 year-old palm, the forage yielded only 411
kg/ha dry matter. The productivity of native pasture has been estimated
conservatively to range from 3 tons/ha/year at establishment to as low
as 435 kg/ha/year in the mature phase (Chen et al. 1991). Figure 2 shows
the changes in dry matter yield of ground vegetation in relation to age
of oil palm and rubber.
|
Figure 2. The forage
dry matter yield in relation to ages of oil palm and rubber. |
Attempts had been made to increase forage productivity
under oil palm and rubber through planting of improved grass species in
the plantations or more recently through modifications of the planting
patterns of the palm/trees to increase light transmission without changing
the total number of trees/ha. Chen et al. (1978) reported planting
guinea grass and stylo under five year old oil palm. But the grass and
legume productivity declined after two years of cattle grazing and improved
species were replaced by native species. Inter cropping of guinea and
napier grasses under rubber were only possible for the first three years
of planting. Yields in second and third year were only 80% of the first
year. However, after five years, the yield dropped significantly low
to only 30% of first year’s yield (Najib 1989) and therefore not viable
to grow improved grasses after five years. Although the production of
improved forages is good in the early stage of the plantation, their poor
persistence and survival have limited their utilization unless proper
management is adopted.
Modifications of planting patterns have been studied in
oil palm and rubber. These modifications are designed to provide a long
term high light environment in the interrows for longer forage productivity.
Double hedge row is a planting pattern in which two rows of oil palm or
rubber are interspaced with a wide open area for pasture without changing
the plant density. In oil palm, the conventional planting was triangular
9.2m x 9.2m x 9.2m with 138 palms/ha. In double hedge row, the planting
pattern was triangular 6.7m x 6.7m x 6.7m interspaced between the two
rows with 15.2 m open space (Abdullah and Shukri 1997). They reported
that with the increased in forage dry matter yield, the double hedge row
system could support 3 to 4 heads of sheep/ha compared to only 2 to 3
sheep/ha under conventional system when the palm were more than 7 years
old.
In rubber, conventional planting patterns were either
6mx4m with 416 trees/ha or 4.8mx4.5m with 462 trees/ha or 9mx2.5m with
444 trees/ha. In the double hedge row planting pattern, trees were planted
in double rows with 2mx3m spacing and the double rows were separated by
wide interrows of 22m. The rubber rows were aligned East-West direction
to intercept maximum light in the interrows. In the wide interrows, improved
pastures were planted instead of the conventional leguminous covers (Chong
and Tajuddin 1994). They showed that early growth and yield of rubber
in double hedge row planting were comparable to those of conventional
planting system. They also reported increased forage yield as well as
increased sheep live weight gains.
Utilization of forages
Under oil palm, animals can be released for grazing 18 to 20 months after
field planting when the young shoot are beyond the reach of the animals.
Grazing management under plantation requires a systematic and flexible
system to equate animals stocking rate with forage availability. Surplus
stock needs to be sold or transferred to another area to avoid deleterious
effects of overgrazing. In young oil palm, 3 Kedah-Kelantan steers/ha
can be kept for two years until they are finished off. An average daily
gain of 320 g/head had been reported. Subsequently the stocking rate
could be adjusted to 2 and 1 Kedah-Kelantan cattle/ha for a period of
2 years when the canopy is closed. Lower carrying capacity of 0.3 to
0.4 Kedah-Kelantan cattle/ha may be adjusted on native pasture depending
on season, soil type, age of oil palm and plantation management (Chen
et al. 1978; Chen et al. 1991).
Sheep had also been successfully integrated with oil palm.
The stocking rate depends on the availability of native forages under
the palm. The recommended stocking rate for 2 to 6 years old palm is
6 to 10 sheep/ha. In terms of animal productivity, local breed of sheep
under oil palm attained weight of 22.2 kg in 9 months compared to 17.9
kg at one year of age under rubber (Abdul Rahman 1987).
Sheep is the most suitable animals to be integrated with
rubber. Cattle and goats can cause damage to the rubber trees because
of cattle’s trampling effects and goat grazing habit. Sheep can be introduced
under immature rubber when the trees are more than two years old and when
the height of the lowest whorl of leaves is more than two metres above
the ground. The recommended stocking rate is 6 to 8 sheep/ha for immature
rubber trees and 3 to 5 sheep/ha for mature trees (Tajuddin and Chong
1988).
A study by Chong et al. (1990) showed that the initial
high level of native forage production under immature rubber (3 years
old) of about 2200 kg/ha could support a high stocking rate of 17 sheep/ha
with animal productivity of about 400 kg/ha/year. However, stocking rate
had to be steadily reduced as forage dry matter yield declined under maturing
rubber trees. In mature rubber (7 years old), native forage availability
was less than 600 kg/ha and this could only support 2 to 3 sheep/ha with
animal productivity of only 72 kg/ha/year.
Meeting the nutritional requirements of ruminant under
declining forage resources in mature plantation is important for livestock
management and production (Wong et al 1988; Chen and Shamsuddin 1991;
Abdullah et al 1997). Low forage availability has been reported to lower
conception rate (52%) of Kedah-Kelantan cows with access to fertile bull
year round and grazing on native forages in 10 to 15 years old oil palm
plantation (Wan Mohamad et al 1987). There was an increasing trend of
anestrous animals towards the end of the second year. Currently, successful
integrated farms use low stocking rate of 0.25 to 0.5 animal unit/ha under
mature trees.
CONCLUSION
In the plantations, plants that grow in the inter rows are considered
weeds by the plantation management and they are controlled by using herbicides.
Only ‘soft grasses’ such as Axonopus compressus, Paspalum conjugatum and
Ottochloa nodusa are tolerated. The average cost of weed control in
oil palm plantation is about RM 100 /ha/year. In the last few years, with
the economic slow down and higher cost of herbicides, and with support
from the government in terms of soft loan to buy cattle, many of the big
oil palm plantations have embarked on the utilization of these ground
vegetation for animal feed by integrating cattle with oil palm. For example,
FELDA Farm products have a total cattle population of over 20,000 and
ESPEK Risda with over 12,000 heads. All these animals are integrated with
oil palm. This environmental friendly technique of weed control using
cattle as grazers has been shown to cut costs in terms of herbicide and
labor costs an estimated 10 to 20% in the first year and up to 30 to 40%
after three years of grazing. Other added advantages of integration are
the additional income from sales of animals and increased yields of the
oil palm mainly due to the recycling of the dung and urine in the plantation.
ACKNOWLEDGEMENT
The author wishes to thank the Director General of MARDI for his permission
to present this paper and to the Director of Livestock Research Centre,
MARDI for his guidance and encouragement. The author is also grateful
to FAO for sponsorship.
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