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Indigenous Bali Cattle: The Best Suited Cattle
Breed for Sustainable Small Farms
in Indonesia
Harimurti Martojo
Laboratory
of Animal Breeding and Genetics,
Faculty
of Animal Science, Bogor
Agricultural University, Indonesia
Introduction
Indonesia
has a total population of around 206 million with 4.5 million households keeping
livestock. About half of the cattle farmers are small farmers.
The
Indonesian archipelago is a land area of 1.8 million km2
consisting of over 13,000
islands stretching from the Western tip of Sumatra to the Eastern border of
Papua. The
largest island, Kalimantan (Borneo), covers 28% of the total land area. Java,
with only 6 –
7% of the total land area, is
inhabited by around 60% of the total population and is the most densely
populated island. The
agro-ecological zones vary from the humid coastal wetland swamps in Sumatra,
Java, South Sulawesi and Bali, to the sub-humid and semiarid dry land in the
eastern part of Java, Sulawesi and most of the Nusa Tenggara islands. There is a wetter to a drier
climate from the west to the east. Approximately 60% of the
archipelago has about 7 –
9
consecutive months of rain in the wet season and less than two months with no
rain in the dry season. The eastern islands have the lowest rainfall with
the dry season varying from 3 to
8 months. The average temperature stays within a constant
range differing in only a few degrees
centigrade
between the hot and cool months. The farming systems are
regulated more by rainfall than temperature. The plantations and food
crop areas are located primarily in the western wetter regions. Extensive
marginal grasslands are in the drier eastern islands. Rain
forest areas are found in Sumatera, Kalimantan and Papua, with limited areas on
Java, Madura, Bali and Sulawesi. An alarming
deforestation process is still occurring caused the illegal logging activities.
The
soil fertility varies greatly, strongly affected by the climate and active
volcanoes found in many of the large and small islands. The
heavy rainfall causes soil erosion and high temperatures resulting in chemical
weathering. The
eastern islands generally have very poor soils that prevent intensive farming. The
animal production systems involve both ruminants and non-ruminants. Crops
and animals are integrated with the benefits associated with the complementary
interactions between these products. The economic benefits of
these integrated systems contribute to their sustainability (Devendra, 1993).
Animal production systems
Only
three major cattle production systems will be described (Devendra et al.,
1997).
1. The extensive grazing systems
These
are primarily low-input-low-output
systems with less opportunity for improvement through the application of new
technologies:
·
Native grassland grazing
·
Upland forest and forest margin grazing
2.
Arable
crop land and pasture combination systems
The
interactions between crops and animals are important in these systems, and the
opportunities for interventions are significant:
·
Roadside and communal grazing combined with stubble
grazing
·
Animals tethered or allowed free access
·
Grasses, crop residues and agro-industrial
by-products stall-feeding
3. Systems integrated with perennial tree crops
·
Grazing under coconut, rubber, oil palm and fruit
trees
In the first major system, the farmers are primarily small
landholders with occasional tribal herds of a few hundred head owned by a
tribal-head. In the second
system, nearly all participants are small landholders. In the third system, the oldest traditional system,
traditional small coconut plantation grazing is practiced. The third system is a relatively new effort, still being
tried, to integrate large commercial plantations (rubber, oil-palm and fruit
trees) with small landholder animal production (small and large ruminants).
Feed
resources
In the Eastern islands, Nusa
Tenggara Barat (NTB) and Nusa Tenggara Timur (NTT), large areas of native
grasslands occur, and are grazed continuously throughout the year by buffalo,
cattle and goats. These
grazing areas are communal and no one is held responsible for the land
maintenance. Most
of these areas currently have fast growing weed infestation problems, namely Chromolaena
odorata. Latest unofficial observations stated that about 80% of the
edible native vegetation in the grazing lands in the NTT are covered by weeds,
creating serious feed resource problems for the cattle and other ruminants.
The overall availability of
feed for the ruminants is probably adequate, however the problem is unequal
distribution. Sumatera
is over-supplied, while deficiencies can be found in Java, Madura, the eastern
Islands and Papua. Trials on forage integration with perennial tree
crops such as the oil palm, rubber and fruit trees are in progress.
Most
cattle feed on the native forages on wastelands, roadsides, unplanted land and
crop-stubble. Cattle are stall-fed year-round in systems that are
more intensive. In
extensive systems, cattle are herded or let out to graze in the natural common
grazing areas during the day and corralled
at night.
The Bali cattle breed
The
Bali breed is one of the four existing indigenous cattle breeds (Aceh, Pesisir,
Madura and Bali) in Indonesia. The Sumban-Ongole and
Javan-Ongole may also be considered local breeds. Although
no official historical records exists, it is generally accepted that the Bali
cattle is the domesticated direct descendant of the wild Banteng still surviving
as an endangered species in three National Wild Reservation Parks (Ujung Kulon,
Baluran and Blambangan) in Java.
Taxonomy of the Banteng / Bali cattle
Many
taxonomical names have been given to the Banteng/Bali cattle. Some
of these names are, Bos sondaicus, Bos
sundaicus, Bos javanicus, Bos bantinger, Bos banten, Bos bantinger, Bibos
banteng and Bibos sondaicus (Merkens, 1926). The last two names using Bibos are based on the opinion that
the Banteng belongs to a separate species (Bibos) from the other cattle groups (Bos).
The
Banteng are more closely related to the Gaur and Gayal. The
earliest documented report on the Banteng was by Schlegel and Muller in 1836 (Merkens,
1926).
They stated that the Banteng was found wild in small
herds with a single bull and several cows and calves in the forests of Java and
Kalimantan (Borneo). The Banteng
is a large animal according to this report. The
bulls have a withers height of 1.76 meters. The
t’Hoen has a smaller wither height of 1.4 to 1.5 meters, and a chest girth of
2.0 to 2.1 meters. There is no recent report on the measurements of
Bantengs still surviving in the Wild Reservation areas. This
is because of the difficulty in catching these animals in the wild. The
few samples in the Zoos in Java have no authentic records of their origin and
dates of capture, casting doubt on whether they were actually wild Bantengs or
just domesticated Bali cattle. The distinguishing
difference between the Banteng and Bali cattle is the size and some behavioral
traits.
The
more recent taxonomical names adopted by the IUCN/SSC Asian Wild Cattle
Specialist Group (Byers et al., 1995), naming three subspecies
of wild Banteng are the Burma banteng (Bos
javanicus birmanicus), the Javan banteng (Bos javanicus javanicus), and the Kalimantan (Borneo) banteng (Bos
javanicus lowii). How many subspecies
should be recognized and included in captive breeding programs remains an
unresolved problem. There is a need to further assess the genetic and
phenotypic variations within the global population of wild Banteng utilizing new
DNA technologies to determine the validity of the above three traditionally recognized subspecies.
Additionally,
there are unresolved questions about the purity of the genetic status of the
captive population.
Many founder animals for the captive populations
were Bali cattle, which is the domesticated form of the wild Banteng. Because
Banteng can interbreed with common cattle, there exists the possibility that zoo
populations may contain genetic material from Bali cattle X Bos
taurus crosses. Domestic and feral Bali
and other breeds of cattle are also a threat to the genetic integrity of wild
Banteng populations in the National Wild Reserves in Java.
Conservation
Both
the IUCN Red Data List and the U.S. Endangered Species Act classify the Banteng
as endangered. This
is based on an overall decline of at least 20% over the last three generations. The
Banteng is not currently listed by CITES, although the IUCN/SSC Asian Wild
Cattle Specialist Group (Byers et al., 1995)
is seeking to have them listed as Appendix I.
There
is no immediate concern for the Bali cattle considering the current total
population estimate of 2.3 million head. There
is some concern about the purity because of intensive crossbreeding programs
using natural mating and AI using exotic breeds that may cause extinction
because of indiscriminate crossing.
Current population estimates
and distribution
The
Banteng
No
subpopulations of more than 500 Banteng are known and only six to eight
subpopulations of more than 50 Banteng are known to remain (five or six on
Java). The population trend on Borneo is unknown. The
Banteng populations on Java are relatively stable, although there are threats
due to illegal hunting, habitat destruction and diseases from domestic
livestock.
The Bali
cattle
The
current population estimates
(of 2000)
for the Bali cattle in the five major resource areas are as follows (Talib et
al., 2002):
Resource area
|
Estimate of population size (in 2000), head
|
Bali
|
529,000
|
NTB
|
377,000
|
NTT
|
443,000
|
South
Sulawesi
|
718,000
|
Lampung
|
255,000 (recently added resource)
|
There are other provinces with
fast growing population numbers managed by small landholders. One
of the most promising provinces is
Southeast Sulawesi with a recent population of 300,000 head. These herds were started
using small numbers of imported Bali cattle in 1923 and larger numbers during
the five-year plans. Propagation was conducted through governmental
owned cattle distribution to participating farmers and redistribution of the
offspring to a growing number of participating farmers. This is another example
of the superior quality of Bali cattle as a pioneer breed for the farming system
in many new cattle production areas (transmigration projects).
There
is however some concern for the negative population growth trend of 12.3% on
average in due to extraction during the monetary crisis years. Measures
to halt this negative trend have been taken by local governments.
The
total populations of the major local breeds are as follows:
Breed
|
Population size, head
|
Ongole
|
1,033,000
|
Bali
|
2,632,000
|
Madura
|
1,131,000
|
others
|
4,980,000 (including exotic and crossbreds)
|
The Bali cattle have the
largest number, showing it as the local cattle breed most suitable for small
landholder cattle farming.
Characteristics
The
Banteng is considered one of the most beautiful of all wild cattle species. They
are most likely the ancestors of the domestic cattle of Southeast Asia. The
Banteng are a sexually dimorphic species, with mature males being dark bluish
black and cows and juveniles reddish brown. Both
sexes have white rump patches and stockings. Both sexes carry horns,
although they are much heavier and larger in the males. The
Banteng are smaller and have a more even temperament than the gaur. There
is a well-defined narrow dark stripe along the backbone, only seen in the calves
and females. In
bulls, the red hair on the body begins to darken at 12 –
18 months of age and by
maturity, the animal becomes almost black. In castrated bulls, the
black hair on the body changes to red again within a few months of castration.
The body is relatively large-framed and well muscled. Adult males weigh between 600 – 800
kg, whiles adult females weigh between 500 – 650
kg. Their average lifespan in the wild is 11 years, although they
can live to 20 –
25 years of age. It
is very common for captive Banteng to live into their late teens or mid-twenties
(Byers et al., 1995). These are humpless
cattle.
Productivity traits of the Bali cattle
The
Bali cattle are similar to the Banteng, differing only in size and temperament. Domestication
has brought about smaller, easier to handle and docile animals. The
average production
traits of the Bali cattle females under the extensive farming system showed in Table 1 (Talib
et al., 2002)
Table 1. Production traits of the Bali cattle females
|
Bali
|
NTT
|
NTB
|
South
Sulawesi
|
Birth weight, kg
|
|
|
|
12.3
|
Weaning weight, kg
|
82.9
|
79.2
|
83.9
|
64.4
|
Yearling weight, kg
|
127.5
|
100.3
|
129.7
|
99.2
|
Weight at puberty, kg
|
170.4
|
179.8
|
182.6
|
225.2
|
Mature cows weight, kg
|
303.3
|
221.5
|
241.9
|
211.0
|
Average mature bull weights for NTB, NTT and South Sulawesi
range 335 –
363
kg and the corresponding weight for the Bali is 395 kg (Talib et al., 2002). Table 2 shows the reproductive performance and milk production of the
Bali cattle (Talib et al., 2002).
|
Bali
|
NTT
|
NTB
|
South
Sulawesi
|
Age
at puberty, yr.
|
2.0
|
2.5
|
2.0
|
2.5
|
Calving
age, month
|
32
|
41
|
36
|
36
|
Calving
interval, month
|
14
|
15.4
|
16
|
15.7
|
Calving rate, %
|
66.3
|
66.6
|
51.7
|
60.4
|
Calf mortality, %
|
8.5
|
48
|
15
|
8
|
Milk prod., kg/6 month
|
274.5
|
165
|
--
|
164
|
Those
average figures for the cows are considered low compared to figures from the Bos
taurus cattle in the intensive production systems in temperate zones.
However,
these figures are the highest among the indigenous cattle breeds in
Indonesia, especially the calving rates. The figures in table 1 and 2 were cited from the latest article presented in an
ACIAR-CRIAS organized Bali Cattle Workshop held in 2002 (ACIAR-CRIAS, 2002). The
data was based on field observations and measurements in four areas from a
limited number of animals. The
measurements are likely influenced by the differences in environmental and
management systems, thus making comparisons between these performances way not valid.
The Unique
pioneering traits
A harsher environment induces smaller/lower performance in
several traits such as lower calf birth weight, low milk production, lower calf
growth rate and
earlier calf age at foraging as well as
cattle health resilience. A
herd will also show lower birth rate (calving percentage/crop) and higher calf
mortality under stressful climatic conditions. The smaller average growth rate and weight at different ages
are also a herd survival adaptation. If necessary, a herd could revert to its wild ancestor feral/wild animal traits to survive in the wild without any human
intervention. The
proof of this can be seen in the feral Bali cattle populations in several
small-uninhabited islands in Indonesia.
The most extreme example of feral Bali cattle is the
thriving population on the Coburg peninsula in Northern Australia.
The
Bali cattle O.
K. a species that has the ability to show different
phenotypes under different circumstances, also known as phenotypic plasticity. This
ability may not be beneficial for intensive management systems. However,
it is favorable for the small landholder system.
Genetic improvement
(Breeding programs)
Pure
breeding, cross breeding and selection programs was applied utilizing local and exotic breeds in Indonesia.
The
following is a concise report on the efforts started in the early 19th
century (Merkens, 1926; Fordyce et al., 2002;
Martojo, 2002).
Ongole and Hissar breeds
Local
breeds (Aceh, Pesisir, Madura, Bali, Javan-Ongole and Sumban-Ongole) were
improved using Ongole bull from India. This
was recorded in the 19th century using Ongole bulls and small sized
local Javan-breeds (now considered extinct) in East Java. Ongole bull imports by several private plantation companies to
produce larger draught cattle continued in small numbers. This
was terminated at the end of the century due to rinderpest disease outbreaks in
India. Massive Ongole cattle importation from India
continued until 1920 on Sumba island. In 1923, the number
amounted to about 1,500
head. Sumba
has been a source of breeding stock for other regions since then. The
Hisar breed was also imported and used in Sumatra and Northern Sulawesi.
Madura breed
Starting
early in the 20th century the Madura breed was maintained pure in
Madura by closing the Madura from other breeds. Trials
were started to propagate Madura cattle in Java and Flores Island. However,
these cattle did not thrive and a gradual change was made to the Bali breed.
The Bali breed
In
1926 the Bali breed numbered 275,000
head in Bali and 125,000
in the Lombok islands. The Bali breed was then distributed to Timor, South
Sulawesi and other regions in the eastern islands. After
a century of effort, the highest population among the other breeds (local and
exotic) totaled 9.8 million head of cattle consisting of 2.6 million head of the
Bali breed. This has proven the superiority of the Bali breed
for most agro-ecological zones in Indonesia. Most
of theses cattle are in the hands of small farmers. The Bali breed is the best for small landholders.
Exotic breeds
Beginning with the second
five-year plan in the 1970’s, frozen
semen from exotic cattle breeds was imported. Many
crossbreeding programs using exotic bulls (Bos
taurus, Bos Indicus and
Bos indicus derivatives) or frozen semen (artificial breeding) in these
regions were failed to yield desirable results. Success
occurred only where zebu or zebu derivative crossbreeding was utilized. It
is likely that such programs will never succeed in the harsh zones unless
adequate fodder availability is assured and the farmers can afford the feed and
concentrates required by the crossbred cattle. Most
of the eastern island regions have plenty of grazing lands, but such lands are
communal and not properly managed. Grazing on these lands
is uncontrolled, leading to poor land productivity. Fodder
cultivation is not in practice in these regions. The
local Bali cattle survive primarily on fodder trees; grasses cut from forests,
or graze in nearby forests. Fodder cultivation is not a priority for the small,
marginal farmers that are the majority in the eastern regions.
Breeding programs
for the small landholder farming system
The
unique conditions in the small landholder cattle farming system has drawn
special attention because efforts to improve productivity by introducing new
technologies developed in the developed world ended in failure. New
breeding approaches (Martojo, 2002; Talib et
al.,
2002), nutrition (Bamualim and Wirdahayati, 2002) and management programs
(Fordyce et al., 2002) were suggested in the ACIAR worshop.
The
most current recommendation was the “Contribution to sustainable livelihood
and development; Realising Sustainable Breeding Programs in Livestock
Production” (INRA and CIRAD, 2002). This
recommendation is based on the presence of three production levels: Level 1 – Subsistence-based
Production, Level 2
– Market-based Production and Level 3 –
High-input Production. The small landholder system fits in Level 1 and requires a special method
for the planning and application of various improvement efforts.
Disease resistance
It is also a known fact that
exotic and crossbred cattle are less resistant to parasitic infestation and diseases in comparison to local
cattle. Poor transportation, communication, and marketing
infrastructure make these regions inaccessible. Extension services are
therefore poorly equipped to meet the requirements for the efficient technology
transfer needed for most input-intensive improved breeds.
Thus,
after several five-year trials plans the government of
Indonesia should have been able to determine a best breeding policy for the best
suited cattle breed for the small landholders system. The
Aceh breed for Aceh province, Pesisir for West Sumatra, Javan-Ongole for
provinces in Java, Madura for Madura province and most importantly the Bali
cattle for the other provinces and the Eastern Islands and Kalimantan were
considered (Borneo).
Weaknesses of the Bali cattle
Despite it’s superior
qualities as a pioneer breed, this breed has weakness. The
Bali breed has a unique susceptibility to the Malignant Catarrhal Fever, which
is contracted through sheep as a vector. In
provinces with a high sheep population, such as West Java, the Bali cattle
cannot survive. Another
disease unique to the Bali cattle is the Jembrana disease. This
disease also has a high morbidity rate. No
economically effective vaccines have been developed for these diseases. Only
Bali cattle originating from Bali island (which may have a higher rate of
inbreeding as a result of decades of isolation due to conservation) and non’ Bali cattle from the other areas (NTT, NTB
and South Sulawesi) have
this susceptibility. This major weakness has not influenced the government against using the
Bali breed to improve existing populations or start new cattle populations
utilizing the Bali breed.
Role of the Bali cattle in small landholder
livelihood
Under harsh environmental
conditions indigenous animals performed much better than the improved stock. It would not be a sustainable practice to improve the genetic
potential of this breed by breeding under artificially improved conditions for
higher production. Scientists and decision-makers in the regional and
central government have underestimated Bali cattle. Local
Bali cattle have been acclimatized over the years in these regions and have been
integrated into the rural small landholder economy in marginal areas for various
reasons. The
important contribution of these cattle has been studied and reported as follows:
·
As source of progeny (calves)
·
Weight gain
·
As a safe deposit (source of cash in emergencies)
·
Insurance for crop harvest failures
·
Draught animal in tillage work and hauling farm
products
·
Manure for fertilizer
The first two roles are
biological production traits most studied and given the highest attention. However,
the second trait may not be important in a harsh environment where survival is
most important and faster growing animals may have a reduced chance for
survival. In the grassland areas where crop planting is
minimal, only the first and third traits are important.
Organic farming system
Environmental issues are
becoming increasingly important internationally. The
indigenous cattle are an important and integral component of the small
landholder cattle production system. This cattle production system is essentially
“organic” in nature and the most sustainable system. The
farmers also prefer indigenous cattle because they are less demanding and less
prone to the problems usually associated with most of the 'improved' and/or
crossbred cattle.
Ecological
or organic farming is seen as an alternative to chemical intensive agriculture. One
of the important points in this direction would be the development of indigenous
technologies for ecological and economical farming methods. It
has not been argued here that
crossbreeding or external genetic interventions are non-sustainable. However,
the rural small landholder regions in Indonesia cannot sustain these
interventions because the agricultural production method in these regions is
essentially low external input in nature. Thus, any external
intervention calling for input-intensiveness would cause ecological imbalances
that damage the long-term sustainability. Policies
re-oriented towards maintaining the indigenous Bali breed and improving their
efficiency, not through external genetic intervention, but through within breed
genetic improvement are required. Effectively harnessing
locally available resources is also an essential requirement.
Conclusions
Based on the facts discussed in this work,
the Bali cattle can be considered the most suitable indigenous cattle breed for
the low-input, high stress production system still practiced by millions of
families in Indonesia.
References
Bamualim, A. and Wirdahayati, R. B. 2002. Nutrition and management
strategies to improve Bali cattle productivity in Nusa Tenggara. In: Proceeding
of an ACIAR Workshop on “Strategies to Improve Bali Cattle in Eastern
Indonesia”, Denpasar, Bali, Indonesia.
Byers, O., Hedges, S. and Seal,
U. S. (eds.). 1995.
Asian
wild cattle conservation assessment and management
plan
workshop. Working document. IUCN/SSC Conservation Breeding Specialist Group,
Apple Valley, Minnesota, USA.
Devendra, C. 1993. Sustainable animal production from small
farm systems in South-East Asia. FAO Animal Production
and Health Paper 106. FAO, Rome, Italy.
pp. 143.
Devendra,
C., Thomas,
D., Jabbar,
M. A.
and Kudo,
H. 1997. Improvement
of livestock production
in crop-animal systems in rainfed
agro-ecological
zones
of Southeast Asia. ILRI (International Livestock Research Institute), Nairobi,
Kenya. pp. 116.
Fordyce, G., Panjaitan, T., Muzani,
H. and Poppi, D. 2002. Management to facilitate
genetic improvement of Bali cattle in Eastern Indonesia. In: Proceeding of an
ACIAR Workshop on “Strategies to Improve Bali Cattle in Eastern Indonesia”,
Denpasar, Bali, Indonesia.
Martojo,
H. 2002. A
simple selection program for smallholder Bali cattle farmers. In: Proceeding of
an ACIAR Workshop on “Strategies to Improve Bali Cattle in Eastern
Indonesia”, Denpasar, Bali, Indonesia.
Merkens, J. 1926. De
paarden en runderteelt in Nederlandsch-Indie.
Landsdrukkerij-Weltevreden,
Nederland.
Talib, C., Entwistle,
K., Sirega,
A., Budiarti-Turner,
S. and Lindsay,
D. 2002. Survey
of population and production dynamics
of Bali cattle and existing breeding programs in Indonesia. In:
Proceeding of an ACIAR Workshop on “Strategies to Improve Bali Cattle in
Eastern Indonesia”, Denpasar, Bali, Indonesia.
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Fig. 1. A
traditional Bali cattle market near Kupang, the capital of Nusa Tenggara
Timur Province
|
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|
|
Fig. 2. An adult Bali
cattle
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Fig. 3. Cattle
market and yellow trucks, transportation tools, in Kupang traditional
Bali cattle market
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Fig. 4. An
adult Bali cow
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