Importance of Scavenging Feed Resource Base (SFRB) for village chicken production is clearly demonstrated by Roberts and Gunaratne (1992) and Gunaratne et al. (1993). Total biomass of the flock is determined by SFRB. If the biomass of the flock exceeded carrying capacity of SFRB, some birds in the population, especially the weaker birds (young chicks) will die. Similarly survival will be more when SFRB is more than the requirement of the flocks. A natural balance is seen between SFRB and biomass of the flock in a given environment unless some intervention is made. SFRB is comprised of household waste, crop by-products, cleaning of gardens, fields and wastelands. In some environments SFRB is relatively constant through out the year and in some others SFRB will fluctuate with factors such as seasonal rainfall, agricultural activities, etc. It should also be noted that in some environments rapid urbanization, development projects and environmental changes are causing restrictions on availability and access to the SFRB. Land area available for scavenging and a distance a flock can travel to scavenge will depend on many factors such as flock size, feed availability, population density, agricultural activities, predators, etc. In addition, behavioral studies have shown that some birds (e.g. unselected) have better scavenging ability compared to others (e.g. crossbred). When crossbred birds were released to scavenging environment, they tend to restrict their scavenging area close to the household.
If the capacity of the SFRB and the seasonal variations are known, more efficient strategies for production by flocks of scavenging village chickens can be developed. Roberts and Gunaratne (1992) described two methods for estimating the capacity of the SFRB for chicken in villages and discussed application to utilize the information obtained. In one method, the following formula was proposed for the calculation of SFRB. For this calculation, measurement and identification of different components in household waste and crop content are required.
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H |
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N |
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SFRB = |
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x |
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where; |
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P |
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N - X |
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H = amount of household waste/family/day (kg dry weight),
P = proportion of the crop content which is household waste as determined by visual inspection,
N = number of families in the community.
X = number of families in the community which do not keep chickens.
In the study of Gunaratne et al. (1993) the figures are:
0.200/ 0.720 x 1/0.5 x 365 = 203 kg dry weight/family/year.
The amount of protein in the SFRB can be determined from an analysis of crop content, and the ME can be determined by analysis of the crop content or by reasonable estimation. On this basis of 11.2 % protein and 3,000 Kcal/kg, the SFRB has 23 kg protein and 609 Mcal metabolizable energy per year.
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Alternatively, the SFRB can be calculated if the weight profile and constitution of the average flock is known, together with the growth rate and hen day production %. To the extent that there is available feed, the amount of feed consumed by the birds is determined by their energy requirement. The protein consumption and availability for maintenance, growth and egg laying, is determined by the percentage protein in the diet. The daily consumption of the flock is the SFRB, so it can be calculated using the formula,
SFRB = ∑Ej / Es where;
j = the average number of birds in the family flock,
Ej = the ME requirement for the daily maintenance and production of each bird per day (kcal/kg dry weight),
Es = the ME in the scavenging feed (kcal/kg dry weight),
'j' can be determined from a census of the family flocks.
'Es' can be measured or reasonable estimated from the crop content.
'Ej' can be calculated for each bird from the production data of growth rate and egg production, using a formula such as that of the National Research Council (1984), below,
ME/bird daily = W0.75 (173-1.95T) + 5.5 ΔW + 2.07 EE
Where;
W = body weight (kg),
T= ambient temperature (°C),
ΔW = change in body weight (g/day),
EE= daily egg mass (g).
An ambient temperature of 26 °C is assumed throughout.
The values for the SFRB calculated from published data from developing countries are;
475 kg/year in Indonesia (Kingston and Creswell, 1982),
390 kg/year in Thailand (Janviriyasopak et al., 1988),
195 kg/year in Sri Lanka (Gunaratne et al., 1993 ), which can be compared with the measured value of 203 kg, above.
High mortalities are recorded in young chickens in villages, but if measures such as creep feeding or feed supplementation are undertaken to increase the survival of the chicks, then the mortality will only be transferred to an another age group, unless the number of eggs incubated is planned to match the capacity of the SFRB. If such plans are made, then the extra eggs which are surplus to requirements for incubation, are available for sale or for consumption.
If the capacity of the SFRB varies seasonally then periods when it is high can be selected for activities such as hatching and rearing, and culling for consumption and sale can be undertaken in anticipation of a reduction in the capacity of the SFRB. On the other hand if it is desirable to maintain the population trough a lean period, then the appropriate feed supplement can be provided.
Alternative production systems can be compared e.g. Comparisons between egg and meat production, in order to optimize the nutritional return, and /or the cash return, from a SFRB of known capacity.
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