Abstract:
The study aimed to assess the major livestock feed resources, dry matter production of major feed
resources, feed requirement, and feed balance in the Erer District of Erer valley, Eastern Ethiopia.
A multi-stage cluster sampling technique was used to select required household heads and data
were collected through designed questionnaires, field observation, focus group discussion and key
informants, formal surveys, and other secondary sources. Available grazing land feed resources
were quantified using the Shannon-Wiener diversity index (H') and evenness or equitability index
(E) based on the cover/abundance value of the species as input data and analyzed using R software
and SPSS version 20 software. Results showed that the average household size of the district is
6.63 ranging from 2 to 15 and the average landholding per household is 2.72±0.11 ha. Of which
63.24% is allocated for cultivated land. The average livestock holding in TLU was found to be
3.58±0.11 per household with the largest share occupied by cattle (2.20±0.09) followed by donkey
(0.42±0.02) in two agro-ecologies of the study area. The major livestock feed resources in the
Woreda were crop residues (44.2%), grazing land (20.8%), crop aftermath (10%), fallow land
(5%), forest (watershed) land (3.3%), fodder trees (3.3%), and other feed (13.3%). A total of 51
plant species and 780 individual plant species belonging to 25 families were recorded from
communal grazing land of the study area, from which, 18 (35.29 %) trees, 29 (56.86 %) shrubs,
and the remaining 4 (7.83%) were herbs. Of the three vegetation types recorded, shrubs were
highly dominate followed by trees and herbs respectively. The most frequently recorded plant
species was Lantana camara, 28.20% with 0.2 relative abundance followed by Psydrax
schimperiana (11.29%). The Shannon diversity index of the highland agro ecology (2.509) slightly
shows less value than lowland agro ecology (2.898) though they have not significantly different
(P>0.05). Livestock holding in TLU and land that was the most important production factor was
significantly different (P < 0.05) across two agro-ecologies of the study area. However, the total
DM production from all feed resources were not significantly different in the two agro-ecologies
(P > 0.05). The largest proportion of feed (515.78 tDM/year, 64.11%) came from crop residues
xv
followed by natural pasture (104.1 tDM/year, 12.94%) and aftermath forage (101.32 tDM/year,
12.59%) for surveyed households. The remaining minimum amount of (19.68 tDM/year, 2.45%),
(24.21 tDM/year, 3.01%) and (39.39 tDM/year, 4.9%) feeds dry matter was obtained from forest
land, fodder trees/shrubs, and fallow land, respectively. The total amount of DM obtained from all
major feed resources was 804.48 tonnes of dry matter per year with an average value of 6.71 tonne
dry matter per year where as the total livestock population of the surveyed households was 429.72
TLU. The total feed DM required for this amount of TLU was, therefore, 971.03 tonnes DM/year
(with a negative balance of 166.55 tonne DM/year). Thus, the total feed available addressed nearly
82.88% of the annual DM requirement which was able to support existing livestock for 9.94
months, and feed shortage suffer livestock only 2.1 months per year. The feed gap was significantly
higher (P<0.05) at lowland (133.96 tDM/year, 80.43%) agro-ecology, than at highland (32.56
tDM/year, 19.57%) agro-ecology. This shortage of feed in the study area has resulted in increased
mortality, reduced milk yield, increased abortion, weight loss, and weakness of any livestock
species as reported by the respondents. The respondents take different measures to overcome feed
shortage and reduce its impact on their livestock. Several households use improved forage
(44.17%) in addition to purchasing feed (24.17%) while others preserve and store feeds (17.5%)
during the time of its high availability Some households, which accounted (for 9.17%) and (5%)
were decreasing livestock size and moving herds to another place respectively to cope with
shortage of feed. The amount of feed DM, which indicated a negative balance in the study site,
needs due attention from all accountable bodies. Alternative means of oversawing of natural
pasture, permanent fodder plantation, developing improved forage and animal species reduction
in addition to efficient utilization and conservation of crop residue should be in place with the
involvement of all stakeholders and development actors.