Evaluation of livestock feed balance under mixed crop–livestock production system in the central highlands of Ethiopia
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Abstract
Background
Livestock production under smallholder mixed crop–livestock (MCL) production systems is constrained by feed shortage and scarcity of land on which to grow feed. Livestock feeds are obtained from different sources including crop residues (CR), grazing lands (GL), crop aftermath, fallow land and purchased. But the contribution of these feed resources and the extent of feed balance at farm level are not quantitatively examined. The study was conducted to assess the major feed resources available and evaluate feed balance for the prevailing livestock in MCL system.
Methods
Feed types and amount available, livestock holding size and feed demand were estimated for 159 smallholder farmers stratified into wealth status, which were selected following a multistage sampling procedure. The feed balance was evaluated as the difference between requirements of livestock (feed demand) and amount of utilizable feed (supply) per year in terms of dry matter (DM), metabolizable energy (ME) and digestible crude protein (DCP).
Results
Regardless of farmers’ wealth status, CR mainly sourced from cereals, particularly barley, contributed more than half of the annual feed supply, followed by GL. The contribution of CR to total feed supply sourced on-farm and purchased combined was 55%. Significant differences in the supply, demand and balance of livestock feed were observed across wealth group of farmers. The wealthier have higher quantities of feed supply and demand, but suffered more in feed insufficiency. Overall, about 51, 19 and 38% annual feed deficit in DM, ME and DCP were observed, respectively. But when the rate is considered based on feed produced on-farm only, the deficit worsened and goes up to 60, 34 and 52% in DM, ME and DCP, respectively.
Conclusions
Expansion of grazing land is not a practical option to increase feed supply. Therefore, increasing food-feed crops production per unit area, conservation of surplus forages, strategic feeding based on productivity and traction services of livestock, purchase of feeds, and increasing livestock off-take during time of scarcity would help to correct the observed feed shortage. Moreover, refinement of the feed balance analysis at specific nutrients level would be compulsory for effective strategic interventions.
Keywords
Debre Berhan Dry matter Metabolizable energy Digestible crude protein Feed balance Feed supply and demand Wealth statusAbbreviations
- ADR
age dependency ratio
- CR
crop residues
- DM
dry matter
- DMD
dry matter demand
- DMI
dry matter intake
- ME
metabolizable energy
- MJ
mega joules
- DCP
digestible crude protein
- kg
kilogram
- t
ton
- hh
household
- GDP
gross domestic product
- GL
grazing lands
- masl
metres above sea level
- MCC
milk collection centres
- MCL
mixed crop–livestock
- n
number of respondents
- SD
standard deviations
- SE
standard errors
- TLU
tropical livestock unit
Background
Ethiopia is an agrarian country known for possession of huge livestock numbers. The total livestock population estimated in millions during the 2014/2015 annual livestock sample survey in the sedentary areas of the country was about 56.7 cattle, 29.3 sheep, 29.1 goats, 2.0 horses, 7.4 donkeys, 0.4 mules, 1.2 camels and 56.9 poultry with total tropical livestock unit (TLU) of 52.9, excluding the non-sedentary three zones of Afar and six zones of Somali Region of the country [1]. Livestock perform economic and social functions both at the national and household levels. Albeit variations among data sources, livestock contribute 15–17% of national gross domestic product (GDP), 35–40% of agricultural GDP and 37–87% of the household incomes [2]. Moreover, livestock contribute to improve the nutritional status and income gain of the people by providing meat, milk, eggs, cheese, butter, etc. and commodities, such as live animals, hides and skins for home use and export, and avert risks in times of crop failures [1, 2].
Despite the huge numbers of possession, the current contribution of livestock to the producers and to the national economy is dismal to its size. It has increasingly been unable to meet the demands for the rapidly growing population [3, 4, 5]. Among the many factors that could explain this disproportionate role of the sector often mentioned are the inadequate quantity and quality of feed supply throughout the year to satisfy the annual demand of livestock [6, 7].
Smallholder farmers in the mixed crop–livestock (MCL) systems keep some form of livestock in conjunction with crop production. However, better soils are allocated for food-feed crops, whereas mountainous, sloppy and less fertile marginal lands, which are naturally vulnerable for soil erosion and land degradation, are left for livestock grazing. Eventually, livestock became more dependent on common feed resources derived from low biomass producing food-feed crops and poorly managed grazing lands (GL). In order livestock to express their productive potentials and increase productivity, the available feed resources should match their demands for dry matter (DM) and nutrients. However, frequently livestock are exposed to seasonal feed shortages both in quantity and quality, especially during the dry season [8]. Moreover, the nutritive quality of native pasture is low especially in dry season and it is much worse for crop residues (CR) owing to the lower content of digestible nutrients [9]. Furthermore, the continuing trends of expansion in cropland cultivation at the expense of GL in the MCL systems have resulted in shrinkage of the area and productivity of GL and reversed the proportional contribution of CR for feed upward.
The need to increase both crop and livestock production from the existing resources requires responsive action throughout the production system. Upon examining the livestock feed resources and feed balance at smallholder farm level, Kassa et al. [10] suggested the possible use of livestock feed balance as potential indicator to assess sustainability of the farms. However, the extent and persistency of feed deficit in rainfed MCL systems in the highlands of Ethiopia described in several previous reports [6, 9, 10, 11, 12] are a formidable challenge for sustained livestock production. A negative feed balance in the MCL system disrupts the interactions between the system components, impairs livestock performance and compromises the potential roles of livestock in driving the economic development. For instance, Kassa et al. [10] reported that better-off and medium wealth groups of smallholder mixed farmers did not produce enough feed more than the poor group to support their livestock in the Harar highlands of eastern Ethiopia. However, it is anticipated that the analysis at farm scale that constitutes the major available feeds and the livestock resources would unveil the prevailing status and hint strategies to address feed shortage problems encountered in the mixed farming systems. In the study area like most other MCL systems areas of Ethiopia, the ongoing land use change from grazing land to other land uses mainly to cropland resulted in shortage of grazing lands. On the other hand, feed obtained as a by-product from crop production on converted land from grazing to cropland is not likely to compensate the feed supply due to the inherently low feed value of crop residues. Moreover, feed from other alternative feed sources is limited. The present study was aimed at assessment of the potential feed resources supply for the prevailing livestock feed demand and evaluate the annual feed balance in the MCL system.
Methods
Description of the study area
Map of Ethiopia showing the location of the study area
Average monthly rainfall, potential evapotranspiration (ET0), maximum (Tmax) and minimum (Tmin) temperatures at Debre Berhan weather station (monthly data averaged from 2000 to 2014)
Rainfed MCL farming is the dominant system carried out primarily to meet the subsistence requirements for most of the farmers with their families in the study area. Small-scale irrigated farming is limited to few farmers with small patchy areas along Beressa River mainly for vegetables. The principal rainfed food-feed crops include barley, wheat, faba bean and field pea. The cereals which covered the largest portion of cropped areas are the major sources of CR for livestock feeding. Cultivations of teff (Eragrostis teff), lentils, chickpea, oats, linseed and vegetables are intermittent on small plots of cropland. Natural GL and CR are the major livestock feed resources, while fallow land, crop aftermath grazing and concentrates are occasionally used feeds [8, 15]. The livestock species reared include cattle, sheep, goats, donkeys, horses, mules and poultry. Cattle production with indigenous and cross-bred animals predominates the livestock production followed by sheep production [8].
Wealth status classification criteria
Description of wealth status grouping criteria generalized based on farmers’ perspectives in the mixed crop–livestock system, central highlands of Ethiopia
No. | Criteria | Wealth categories | ||
---|---|---|---|---|
Better-off | Medium | Poor | ||
1 | Cropland holding (ha) | >1.50 | 1–2.5 | 0.25–1.5 |
2 | Number of ploughing oxen | >2 | ≥2 | ≤1 |
3 | Number of milking cows (local and crossbreds) | >2 most of crossbreds | At least 2, few crossbreds | <2 and usually local breeds |
4 | Number of sheep (adults) | 10–50 or more | 5–20 | ≤10 |
5 | Number of equines (adults) | A mule, a horse and donkeys | At least horse and donkeys | No mule & horse may be donkey |
6 | Roof of houses | |||
Corrugated iron sheet | Yes | Yes (often) | No | |
Grass thatched | Yes | Yes | Yes | |
7 | Annual food production and supply to sustain household | Enough with more surplus | Enough but meagre surplus | Not enough, in need of support |
Survey design and data collection
Sampling procedures and sample size
A multistage sampling procedure was employed to select sample farmers engaged in MCL farming and deliver fluid milk to the nearby milk collection centres (MCC). Debre Berhan milkshed was purposely selected based on its accessibility and potential representativeness of the MCL system in central highlands of Ethiopia. From 48 villages in the milkshed, six representative MCC (Wushawushign, Angolela, Kormargefia, Kebele01, Kebele07 and Kebele09) were selected using simple random sampling procedure. Farmers sample size was determined using G * power 3.1.7 software considering the farmer wealth group as fixed effect and assuming 0.25 effect size, α = 0.05 and 80% power of the statistical test [16]. List of farmers obtained from the selected MCC was categorized into three wealth groups to form the sampling frame. The number of sample farmers in each wealth group was based on the ‘probability proportional to size’ sampling technique [17]. Finally, a total of 159 farmers (50 in the poor, 58 in the medium and 51 in the better-off wealth groups) were selected using systematic random sampling with whom the questionnaires were administered.
Data collection
A socio-economic survey using pretested semi-structured questionnaires was carried out using a face to face interview in 2014 and 2015. The questionnaires covered data on: household demographic characteristics, land and livestock ownership, livestock species composition and herd structure, feed types, area of private and communal GL, types of food-feed crops produced, area cultivated, input used and crop yield at farm level. Focus group discussions were conducted with farmers at each of the selected MCC. A total of 40 farmers (6–8 per session) representing wealth groups have participated in six sessions. Knowledgeable farmers from all wealth groups were selected anticipating an effective communication between the moderator and within themselves. The secondary data were extracted from previous studies and information documented at agricultural development and research offices. Local climate data were obtained from Debre Berhan agricultural research centre. Data enumerators recruited from agricultural development agents were trained to assist on primary data collection during face to face interview and group discussions.
Estimation of annual feed availability (supply)
Estimation of livestock feed requirements (demand)
Livestock holdings per household were aggregated into TLU considering the annual average livestock ownership derived based on the number of animals at the beginning and end of the study year. This was done to take into account the annual inflow and outflow dynamics of livestock at famer level. Species-specific TLU conversion factors of 0.7 for cattle, 0.1 for sheep and goats, 0.5 for donkeys and 0.8 for horses were used [25]. The dry matter demand (DMD) was estimated based on the expected daily dry matter intake (DMI) suggested for the standard TLU of 250 kg at 2.5% of the body weight, which is equivalent to 6.25 kg/day or 2280 kg/year [25]. Comparable rate of DMI was also suggested by [26]. The ME and DCP requirements for maintenance were calculated according to the daily average recommendations given by [26]. Based on metabolic body weight, 118.0, 93.0 and 103.45 kcal of ME/W kg 0.75 and 2.86, 1.72 and 2.51 g of DCP/W kg 0.75 per day for cattle, sheep and goats, respectively, were used for maintenance [26]. Accordingly, the daily nutrient requirement tables for maintenance recommended for ruminants in developing countries by [26] were used to estimate the annual ME and DCP requirements for cattle, sheep and goats. In the case of donkeys and horses, the daily ME and DCP maintenance requirements of 14.9 and 27.6 MJ and 0.18 and 0.37 kg recommended by McCarthy as cited in [9] were used, respectively. Then, farm level DM, ME and DCP requirements for maintenance per year were extrapolated relative to the livestock ownership per household.
Livestock feed balance
Livestock feed balance at individual farmer level over the entire production year was determined as the difference between the annual feed DM, ME and DCP supply estimated from major feed resources and the annual feed DM, ME and DCP demands for the annual average livestock holding of farmers.
Statistical analysis
Results
Farm households and key farm resources characteristics
Households demographic and key farm resources characteristics in the mixed crop–livestock system, central highlands of Ethiopia
Households and farm resources characteristics | Wealth groups | Total (n = 159) | ||
---|---|---|---|---|
Poor (n = 50) | Medium (n = 58) | Better-off (n = 51) | ||
Family size | 4.9 (2.0) | 6.2 (1.5) | 6.4 (1.6) | 5.9 (1.8) |
Labour force (in adult equivalent) | 2.5 (1.2) | 3.5 (1.1) | 3.8 (1.1) | 3.3 (1.3) |
Age dependency ratio (ADR) | 1.0 (0.6) | 0.7 (0.5) | 0.6 (0.5) | 0.8 (0.6) |
Livestock holding (TLU) | 5.1 (1.2) | 8.2 (2.0) | 12.0 (2.4) | 8.5 (3.4) |
Cattle | 3.0 (0.9) | 4.6 (1.2) | 6.4 (1.4) | 4.7 (1.2) |
Sheep and goats | 0.9 (0.5) | 1.7 (0.8) | 2.7 (1.2) | 1.8 (1.1) |
Equines | 1.2 (0.7) | 1.9 (1.0) | 2.9 (1.0) | 2.0 (1.1) |
Cropland entitled (ha) | 1.1 (0.5) | 1.3 (0.6) | 1.8 (0.6) | 1.4 (0.6) |
Fallow land (ha) | 0.1 (0.1) | 0.1 (0.2) | 0.3 (0.3) | 0.2 (0.3) |
Cultivated and grazing land (ha) | 2.3 (0.4) | 3.2 (0.7) | 4.1 (0.7) | 3.2 (1.0) |
Cropland cultivated (ha) | 1.6 (0.4) | 2.2 (0.6) | 2.5 (0.6) | 2.1 (0.6) |
Grazing land (ha) | 0.7 (0.2) | 1.0 (0.4) | 1.6 (0.5) | 1.1 (0.5) |
Food-feed crops production
Area of plots of cropland allocated, proportion of farmers who grow the specific food-feed crop types and grain yields per household in the mixed crop–livestock system, central highlands of Ethiopia
Area cultivated, grain yield and proportion of farmers who grow | Wealth groups | Total (n = 159) | ||
---|---|---|---|---|
Poor (n = 50) | Medium (n = 58) | Better-off (n = 51) | ||
Land allocated (ha) | ||||
Barley | 0.9 (0.3) | 1.1 (0.6) | 1.2 (0.4) | 1.1 (0.5) |
Wheat | 0.3 (0.2) | 0.3 (0.2) | 0.5 (0.3) | 0.4 (0.2) |
Faba bean | 0.4 (0.2) | 0.6 (0.3) | 0.7 (0.4) | 0.6 (0.3) |
Field pea | 0.1 (0.1) | 0.1 (0.1) | 0.1 (0.1) | 0.1 (0.1) |
Farmers who grow (%) | ||||
Barley | 100.0 | 100.0 | 100.0 | 100.0 |
Wheat | 78.0 | 93.1 | 100.0 | 90.6 |
Faba bean | 100.0 | 100.0 | 92.2 | 97.5 |
Field pea | 20.0 | 43.1 | 49.0 | 37.7 |
Grain yield (t/hh) | ||||
Barley | 1.7 (0.7)a | 2.1 (1.0)ab | 2.5 (0.9)c | 2.1 (0.9)*** |
Wheat | 0.5 (0.4)a | 0.7 (0.4)ab | 1.2 (0.7)c | 0.8 (0.6)*** |
Faba bean | 0.6 (0.3)a | 0.9 (0.5)bc | 1.0 (0.5)c | 0.8 (0.5)*** |
Field pea | 0.1 (0.2) | 0.2 (0.2) | 0.2 (0.2) | 0.1 (0.2)NS |
Types and availability of feed resources
Feed resource types and estimated quantities of DM, ME and DCP obtained per year per farm household in the mixed crop–livestock system, central highlands of Ethiopia
Feed resource types | Wealth groups | Total (n = 159) | ||
---|---|---|---|---|
Poor (n = 50) | Medium (n = 58) | Better-off (n = 51) | ||
DM (t/hh) | ||||
Crop residues | 3.8 (1.2) | 5.1 (1.4) | 6.6 (1.9) | 5.2 (1.9) |
Barley straw | 2.3 (0.9) | 2.8 (1.3) | 3.4 (1.2) | 2.8 (1.2) |
Wheat straw | 0.7 (0.6) | 0.9 (0.5) | 1.6 (1.0) | 1.1 (0.8) |
Faba bean straw | 0.7 (0.4) | 1.2 (0.7) | 1.5 (1.0) | 1.1 (0.8) |
Field pea straw | 0.1 (0.2) | 0.2 (0.2) | 0.2 (0.2) | 0.2 (0.2) |
Grazing land | 1.1 (0.3) | 1.6 (0.5) | 2.1 (0.5) | 1.6 (0.6) |
Fallow land | 0.1 (0.2) | 0.1 (0.3) | 0.4 (0.4) | 0.2 (0.4) |
Crop aftermath | 0.6 (0.2) | 0.8 (0.2) | 0.9 (0.2) | 0.8 (0.2) |
Purchased | 0.7 (0.5) | 1.9 (1.7) | 2.5 (2.0) | 1.7 (1.7) |
ME (‘000 MJ/hh) | ||||
Crop residues | 28.4 (9.3) | 38.1 (10.8) | 48.8 (14) | 38.5 (14) |
Barley straw | 18.3 (7.4) | 22.2 (10.4) | 26.7 (9.5) | 22.4 (9.8) |
Wheat straw | 4.6 (3.8) | 5.9 (3.2) | 10.3 (6.5) | 6.9 (5.2) |
Faba bean straw | 4.7 (2.5) | 8.7 (4.9) | 10.4 (7.1) | 8.0 (5.7) |
Field pea straw | 0.8 (1.7) | 1.2 (1.6) | 1.3 (1.5) | 1.1 (1.6) |
Grazing land | 9.0 (2.6) | 12.6 (3.7) | 17.2 (4.4) | 12.9 (4.9) |
Fallow land | 0.7 (1.5) | 1.1 (2.6) | 3.4 (3.4) | 1.7 (2.9) |
Crop aftermath | 4.4 (1.2) | 5.7 (1.8) | 6.5 (1.6) | 5.6 (1.7) |
Purchased | 5.0 (3.9) | 13.6 (12.3) | 18.6 (14.8) | 12.5 (12.6) |
DCP (kg/hh) | ||||
Crop residues | 128.8 (42.0) | 182.7 (51.2) | 230 (70.8) | 180.9 (68.7) |
Barley straw | 68.3 (27.7) | 83.0 (38.8) | 100 (35.4) | 83.8 (36.6) |
Wheat straw | 18.4 (15.1) | 23.6 (12.5) | 41.0 (25.7) | 27.5 (20.7) |
Faba bean straw | 35.8 (18.6) | 66.1 (37.1) | 78.5 (53.7) | 60.5 (42.7) |
Field pea straw | 6.4 (13.7) | 10.1 (12.8) | 10.5 (11.9) | 9.1 (12.9) |
Grazing land | 70.1 (20.4) | 98.0 (28.7) | 134 (34.2) | 100.8 (38.1) |
Fallow land | 5.4 (11.5) | 8.2 (20.4) | 26.5 (26.3) | 13.2 (22.2) |
Crop aftermath | 11.4 (3.1) | 15.0 (4.2) | 16.9 (4.0) | 14.5 (4.4) |
Purchased | 36.4 (28.6) | 99.3 (90.2) | 136.0 (108.5) | 91.3 (92.4) |
Livestock feed supply, demand and feed balance
Mean annual livestock feed supply, demand and balance per household in the mixed crop–livestock system, central highlands of Ethiopia
Feed supply, livestock demand and feed balance | Wealth groups | Total (n = 159) | ||
---|---|---|---|---|
Poor (n = 50) | Medium (n = 58) | Better-off (n = 51) | ||
DM demand (t/hh) | 11.6 (0.4)a | 18.7 (0.6)b | 27.4 (0.8)c | 19.3 (0.6)*** |
DM supply (t/hh) | ||||
On-farm | 5.6 (0.2)a | 7.6 (0.2)b | 10.0 (0.3)c | 7.7 (0.2)*** |
On-farm and purchased | 6.3 (0.2)a | 9.4 (0.4)b | 12.6 (0.4)c | 9.5 (0.3)*** |
Balance (t/hh) | ||||
On-farm | − 6.0 (0.5)c | − 11.2 (0.7)b | − 17.4 (0.7)a | − 11.5 (0.5)*** |
On-farm & purchased | − 5.3 (0.5)c | − 9.3 (0.7)b | − 14.8 (0.7)a | − 9.8 (0.5)*** |
ME demand (‘000 MJ/hh) | 54.9 (1.8)a | 86.4 (2.7)b | 122.8 (2.9)c | 88.1 (2.6)*** |
ME supply (‘000 MJ/hh) | ||||
On-farm | 42.5 (1.5)a | 57.5 (1.9)b | 75.9 (2.2)c | 58.7 (1.5)*** |
On-farm and purchased | 47.5 (1.7)a | 71.0 (2.7)b | 94.4 (3.3)c | 71.1 (2.1)*** |
Balance (‘000 MJ/hh) | ||||
On-farm | − 12.3 (2.5)c | − 28.9 (3.4)b | − 46.9 (3.1)a | − 29.5 (2.1)*** |
On-farm and purchased | − 7.3 (2.6)cb | − 15.4 (3.8)b | − 28.3 (3.5)a | − 17.0 (2.1)*** |
DCP demand (kg/hh) | 392.2 (14.6)a | 630.4 (23.5)b | 907.1 (21.8)c | 644.2 (20.2)*** |
DCP supply (kg/hh) | ||||
On-farm | 215.7 (6.8)a | 303.9 (9.3)b | 407.4 (11.8)c | 309.4 (8.2)*** |
On-farm and purchased | 252.1 (8.3)a | 403.1 (16.3)b | 543.4 (21.9)c | 400.6 (13.3)*** |
Balance (kg/hh) | ||||
On-farm | − 176.4 (16)c | − 326.5 (24.7)b | − 499.7 (17.3)a | − 334.9 (15.5)*** |
On-farm and purchased | − 140.0 (16.9)c | − 227.2 (26.4)b | − 363.7 (20.2)a | − 243.6 (14.6)*** |
Percentages of dry matter (a), metabolizable energy (b) and digestible crude protein (c) supply and demand balances of farm households categorized into wealth groups in the mixed crop–livestock system, central highlands of Ethiopia
Numbers and proportions of farmers with positive livestock feed balance in the mixed crop–livestock system, central highlands of Ethiopia
Feed nutrients | Feed sourced from | Wealth groups | Total (n = 159) | ||
---|---|---|---|---|---|
Poor (n = 50) | Medium (n = 58) | Better-off (n = 51) | |||
DM | On-farm | 0 (0.0) | 0 (0.0) | 0 (0.0) | 0 (0.0) |
On-farm and purchased | 2 (4.0) | 0 (0.0) | 0 (0.0) | 2 (1.3) | |
ME | On-farm | 15 (30.0) | 3 (5.2) | 0 (0.0) | 18 (11.3) |
On-farm and purchased | 23 (46.0) | 17 (29.3) | 7 (13.7) | 47 (29.6) | |
DCP | On-farm | 2 (4.0) | 0 (0.0) | 0 (0.0) | 2 (1.3) |
On-farm and purchased | 7 (14.0) | 7 (12.1) | 0 (0.0) | 14 (8.8) |
Relative contribution of feed resources
Relative contributions of feed resources a obtained on-farm and b obtained on-farm combined with purchased feeds to the total annual livestock feed dry matter supply in the mixed crop–livestock system, central highlands of Ethiopia
Seasonal feed resources availability
Seasonal availability of feed resources as perceived by farmers in the mixed crop–livestock system, central highlands of Ethiopia. Availability of feed over the year on a scale of 0–10, where 10 = excess feed available, 5 = adequate feed available and 0 = no feed available
Discussion
Household characteristics and farm resources: implications on livestock feed availability
The overall average family size of 5.86 in the present study is higher than the national average of 5.14 reported by [28], which is closer to the poor but lower than the wealthier group of farmers in the study area. It is still much higher compared to the average family size for both the Amhara Region of 4.62 and the North Shewa Zone of 4.45, where the study site is located [28]. The lower family labour force availability among the poor farming families than the other wealth groups could be explained by the observed small number of family size coupled with higher age dependency ratio attributed to the presence of more productively inactive dependent family members, especially children under 15 years of age. The age distribution of family members and the consequent state of age dependency ratio, particularly among the poor farming families, are in agreement with the national demographic characteristics reported by [1], which explains that about 45% of the population are under 15 years of age, reflecting the dominance of young section of the population with less contribution to the farming labour force requirement.
Availability of farm resources such as family labour, land and livestock has an influence on the level of production and availability of CR for livestock feeding. The limited availability of family labour force in the poor family group may have restrained their capacity to intensify human labour use in the farming operation, which may negatively contribute to the cause for lower farm productivity. It influences farmers to apply adequate labour input for optimum agronomic activities like tillage frequency, timely land cultivation and weeding that are required to increase crop biomass productivity. In addition, farming families with small size of cropland ownership are hardly able to diversify and increase the crop grain yield and associated CR biomass production due to limitation of available cropland and subsequent allocation of smaller plots for the intended crop types. Moreover, the small number of livestock ownership, especially oxen among poor farming families, has a limiting influence on the use of needed animal labour for traction services, such as timely cultivation of cropland with optimum tillage frequency required for the crop type grown. On the contrary, wealthier farming families with relatively better availability of ploughing oxen are able to cultivate their cropland adequately in time and acquire additional cropland for share cropping from other farmers through local lease agreement and attain more feed from the share of CR attained in part or as a whole depending on the agreement with the cropland owners. In support of the present study, several studies reported that inadequate cropland preparation due to limited access to production factors such as land, human and animal labour affect the food-feed crop biomass production [29, 30, 31, 32]. The wealthier are also relatively more efficient in collecting hay from private GL and store for later use in times of scarcity or practice strategic feeding by providing for the more productive animals such as milking cows and working oxen [8, 9].
Types and availability of feed resources
The types and amount of feed obtained per household depend on land use, size of land ownership and cropping pattern during the production season. Irrespective of wealth status, large proportion of land is allocated for crop cultivation than other land use types including grazing, which is in agreement with reports of [14, 6]. The increasing expansion of land cultivation for crop production at the expense of GL has resulted in shrinkage of the area and productivity of GL [14]. Consequently, CR generated from production of food-feed crops comprise the largest proportion of livestock feed resources. In agreement, [33] reported the progressive decline of GL and the use of CR as the major source of livestock feed particularly during the dry season in the mixed farming system of the Bale highlands of Ethiopia. In addition, [9] also observed the heavy reliance of farmers at Debre Derhan in the central highlands of Ethiopia on CR for feeding their livestock.
Besides the suitability of the local agro-climate for barley growing [8, 14], the higher quantity of barley straw collected is associated with the preference of farmers and the consequent allocation of larger plots of cropland for the barley crop cultivation. Apparently, the remaining smaller plots of land are shared for other crop types, which correspondingly leads to lesser quantity of straw obtained from crop types such as wheat, faba bean and field pea. In line with the present study, [33] explained the variation in the quantity and quality of CR produced could be due to the cropping intensity besides the variations in altitude, soil type and rainfall patterns where the crop has been grown.
In relation to the size of cropland ownership and parcel allocated to a specific crop type, higher volume of biomass is harvested by better-off and medium wealth groups than poor farmers. This crop biomass productivity is accordingly translated into the higher amount of CR harvest which reflected the gradient of farmers’ wealth status. In addition to the plot of cropland allocation, the availability of family labour force, size of livestock owned particularly oxen, natural fertility of the cropland and other variable factors associated with the capacity of farmers to afford various inputs and manage timely agronomic practices influence the volume of CR produce per household. Moreover, the amount of feed derived from the crop field in the form of crop aftermath grazing is intrinsically influenced by the cropping pattern and plot of cropland allocation, as part of the feed recovered, is the remainder of the parent crop obtained after harvest in addition to the different weeds and other herbaceous plants grown on the crop field. In line with this, [34] reported the quantity and quality of stubble left varies considerably depending on the harvesting techniques applied for the various crops and the grass weeds grown underneath the main crop. Therefore, it is predictable that the wealthier could be able to benefit more than the poor farmer groups from crop aftermath grazing which is attributed to the larger size of cropland ownership.
The size of available GL in the study area is small irrespective of wealth status, though the wealthier are more favoured to exploit available feed resource from freely grazing the communal land due to ownership of relatively larger livestock herd size. Moreover, fallow lands as livestock feed source were very rare, as there is critical land shortage for crop cultivation as well. In agreement, [34] reported that it was in the past that GL, hay and fallow land grazing were the main sources of feed; however, at present the situation has changed due to the rapidly increasing human population and expansion of crop production in the grazing areas. Same author asserted that there is very little that livestock can forage from the limited communal grazing due to continuous grazing and the mismatch between the feed supply potential of the land and the number of animals kept. Consequently, crop residues are increasingly becoming the main sources of livestock feed resources in the MCL systems [34, 35, 36]. Other several studies have also disclosed that, in recent years, GL in the MCL systems are devastatingly overstocked and that the herbage biomass productivity is declining both in quantity and quality [8, 11, 37, 38, 39, 40]. Therefore, expansion of GL to increase feed availability is not a practical option as the increasing trends of both the human and livestock population are going to claim more additional land further for crop production, settlement and feed sourcing.
Hence, strategic options to improve the availability of CR and other alternative and/or additional feed resources should be intervened. From evidences captured in the present study which are supported by several other findings, most of smallholder farms in the MCL systems are dependent on CR as the main source of feed for livestock. Moreover, nowadays straws have also become an important source of revenue [34] and used for other purposes that compete livestock feed supply. References [41, 34] suggested close collaboration of crop and livestock scientists aimed at multidimensional crop improvement to increase the quantity and feeding value of CR without negatively affecting the grain yield and quality. In addition, Tolera [34] further suggested the introduction of cover crops that could be grazed after short rainy season, high yielding forage crops with possibility of multiple harvests per year and multipurpose leguminous trees used as supplemental green fodder could be explored to alleviate the feed shortage pertaining to the existing situation. In addition, interventions to increase feed biomass per unit area of GL, proper grazing management and purchase of supplemental feeds whenever possible would be among the options that help to reduce the influence of feed shortage on livestock health and productivity.
The fluctuations in the seasonal availability of major feed resources are mainly associated with the rainfall distribution and cropping pattern of food-feed crops. Crop residues are plenty during the dry season, which is the period of threshing for harvested crops. Availability and utilization of crop aftermath grazing is aligned with harvesting periods of crops in the dry season. Crop residues and hay are also conserved for mitigating feed shortage, especially during peak periods of cropland ploughing in the wet season. Forages from grazing lands and fallow lands are available following the main/long and short rainy seasons, when the moisture is sufficient enough to support plant growth.
Livestock feed demand and feed balance
In the present study, livestock feed balance evaluated is generally found to be negative irrespective of farmers’ wealth status, indicating the critical feed shortage in the system to fulfil the DM, ME and DCP requirement for the prevailing livestock. Overall, only about 49, 81 and 62% of DM, ME and DCP requirements are fulfilled, respectively, with the current amount of feed supply from on-farm production combined with purchased feeds. Several previous study findings support the present report in that in the MCL system where land is limited, the contribution of CR is prominent and GL are deteriorating in size and productivity, and the livestock production is performed under annual feed deficit. For instance, Wondatir et al. [9] reported that around Debre Birhan the annual feed supply only satisfies 64% of the maintenance DM 81% ME and 66% DCP requirements of the animals per farm. Study by Amsalu et al. [11] in Gummara-Rib watershed of the Lake Tana sub-basin in Amhara Region shows that the available feed sources address only 72% of the annual DM requirement per household. These studies confirmed the long-standing impediments for increasing livestock productivity consistently claimed by smallholder farmers and development practitioners in the MCL systems, where seasonal feed shortage both in quality and quality coupled with inadequate successful interventions, which are remained unabated.
This study and others mentioned here used same amount of average daily DMI for a standard TLU of 250 kg at 2.5% of live body weight suggested by [25], which is 6.25 kg/day, to arrive at an aggregated demand for feed DM at household level per year. However, the daily DM feed intake is affected by various animal and feed-related factors. FAO [42] described where there is good access to feed, and health and welfare are optimum, the DM intake for young ruminant animals is likely to be 4% of body weight and decline to 2–2.5% as animals are getting mature. Moreover, where feeds of low digestibility are the main or only sources, voluntary intake will be significantly influenced due to the longer time it takes to progress through the digestive tract, and as a result low digestibility is reflected in lower intakes.
Livestock feed balance reported under smallholders in the MCL system is frequently negative [10, 43, 44], and even so many times declared as below the maintenance requirements [6, 9, 11]; however, in fact livestock continued to survive, reproduce, provide and perform their vital functions, whereas the different products and services obtained cannot be imagined at maintenance requirement level let alone when an overwhelming annual feed deficit below maintenance is revealed. Hence, series of critical questions could arise on the assumptions, methods and validations of livestock feed balance estimations, which were also iterated by Kassa et al. [10]. For instance, is the suggested daily DMI amount at 2.5% of live body weight is limited to only satisfy the maintenance requirement, as described in various livestock feed balance studies? To what extent the suggested daily allowance fulfils the animal requirement? Do feed types of any quality and form can be ingested at the suggested rate by any type and/or class of livestock throughout all seasons of the production year? Is that amount of feed could be affordable daily by smallholders in the MCL system consistently throughout the production year? etc.
The feed balance results should be cautiously interpreted, in that the livestock production system is running in an annual feed deficit does not mean that the livestock are currently without any benefit to offer. It is not unimportant either, since it quantitatively unveils the picture of what farmers and experts claim to be the most important determining factors of livestock production, which are feed shortage and the increasing trend of land scarcity on which to produce livestock feed. First of all, the suggested rate for the DMI of feed does not indicate the quality of the feed supplied but the average quantity that the animals could potentially consume daily. In addition, it does not mean that whatever is ingested is equally available to all types of animals. This is because the nutritional requirement of an animal depends on several factors: species, size, age, weight, physiological status (pregnancy, lactation, etc.), level of production (rate of gain, amount of milk produced, etc.), general health, amount of work, weather condition and season [19, 42, 45].
Secondly, there is a need to closely observe the dynamics of farm elements and situation analysis throughout the production year. Actually, the feed balance estimate showed the situations aggregated on annual basis, as if the feed availability and livestock DM, ME and DCP requirements per day are distributed evenly throughout the production year. However, a lot of dynamics can happen in the seasonal feed sources availability, nutritional composition and quality, and in the individual animal body and in the livestock herd in the course of the annual production process. It is an established fact that quantity and quality of feed available from natural pasture are affected by season [10, 35, 43, 44, 45, 46]. Feed sourced from crop production is also affected by type of crop, cropping pattern, amount of input used like fertilizers and agronomic practices applied [36, 47, 48]. Different feed sources of varied quantity and quality may be available to livestock across different seasons, which could be produced on-farm or purchased depending on the capacity of producers to afford. The animals may undergo the phenomenon of compensatory growth, i.e. lose weight during periods of feed scarcity and put on weight (gain) during times of good feed availability. In the meantime, livestock could deliver any forms of products and services during periods of feed availability and/or mobilize what is deposited during good times of the year. At herd level, an inflow from natural perpetuation and purchase of animals, and an outflow due to death, sell and slaughter, and shared rearing of animal in either case could all happen within the year following the scarcity and availability of feed at household level. Hence, the seasonal feed availability coupled with farmers feeding practice and coping mechanism of feed shortage, the productivity gain or loss and the inflow and outflow dynamics of livestock at household level should be considered, while interpreting the livestock feed balance.
Conclusions
The available annual feed dry matter, metabolizable energy and digestible crude protein supplies and requirements of livestock did not match at present, in the study area characterized by smallholder mixed crop–livestock production system. Livestock feed insufficiency unanimously affects the whole group of smallholder farmers irrespective of wealth status. However, the wealthier group of farmers which owned larger size of livestock collected more quantity of feed on-farm and acquired additional feed through purchase found to suffer more in terms of feed deficit than the poor farmers, when livestock feed balance was assessed. Scarcity of GL due to expansion of cultivation on GL coupled with low productivity of biomass from grazing and food-feed crops production further exacerbate the mismatch between feed supply and demand. The trend of land scarcity testifies that smallholder livestock production in the MCL system is likely to continue to rely upon CR. Crop residues which are claimed to have suboptimal feeding value due to the high fibre content and low digestibility comprised the major portion of annual feed supply, and thus the inherent limitations of CR should not be ignored. Farmers who promoted cross-breeding of local animals with breeds of temperate origin to increase milk production are found unable to supply sufficient quantity and quality of feed to achieve the anticipated level of productivity. The present evidences implied that unless the feed deficit is relieved through increasing the availability and quality of feeds and practicing strategic feeding the productivity of livestock will be more profoundly affected.
Notes
Authors’ contributions
MBT designed the study, collected and analysed the data and drafted the manuscript. AMW and BTM supervised the design of the study and data analysis and revised the manuscript. All authors read and approved the final manuscript.
Acknowledgements
The authors like to acknowledge Addis Ababa University and Debre Berhan University for financial support. The authors like to thank staff of the Bosona Worana and Angolela ena Tera district agriculture and rural development offices, development agents who assisted in data collection and farmers of the study area for their cooperation.
Competing interests
The authors declare that they have no competing interests.
Authors’ information
MBT is a lecturer (M.Sc. in animal production) in Debre Berhan University and a Ph.D. candidate in animal production in Addis Ababa University. AMW is an associate professor (Ph.D. in animal nutrition) in the Department of Animal Production, College of Veterinary Medicine and Agriculture, Addis Ababa University. BTM is a professor (Ph.D. in animal nutrition) and head of Animal Production Department in the College of Veterinary Medicine and Agriculture, Addis Ababa University.
Availability of data and materials
The datasets used and/or analysed during the current study are available from the corresponding author on reasonable request.
Consent for publication
Not applicable.
Ethics approval and consent to participate
Not applicable.
Funding
Funding for this study was provided by Addis Ababa University and Debre Berhan University. Both Universities had no role in the study design, collection, analysis or interpretation of the data, writing of the manuscript, or the decision to submit the paper for publication.
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References
- 1.Central Statistical Agency of the Federal Democratic Republic of Ethiopia (CSA). Agricultural sample survey in 2014/15. Report on livestock and livestock characteristics (Private Peasant Holdings). Addis Ababa, Ethiopia; 2015.Google Scholar
- 2.GebreMariam S, Amare S, Baker D, Solomon A, Davies R. Study of the Ethiopian live cattle and beef value chain. ILRI Discussion paper 23. Nairobi, Kenya; Addis Ababa, Ethiopia: International Livestock Research Institute (ILRI); 2013.Google Scholar
- 3.Swanepoel F, Stroebel A, Moyo S. The role of livestock in developing communities: Enhancing multifunctionality. Bloemfontein, South Africa: The Technical Centre for Agricultural and Rural Cooperation (CTA); 2010.Google Scholar
- 4.Shapiro BI, Gebru G, Desta S, Negassa A, Nigussie K, Aboset G, et al. Ethiopia livestock master plan, roadmaps for growth and transformation, a contribution to the growth and transformation plan II (2015–2020). Ethiopia: Addis Ababa; 2015.Google Scholar
- 5.Asresie A. Contribution of livestock sector in Ethiopian economy: a review. Adv Life Sci Technol. 2015;29:79–91.Google Scholar
- 6.Assefa D, Nurfeta A, Banerjee S. Assessment of feed resource availability and livestock production constraints in selected Kebeles of Adami. Afr J Agric Res. 2013;8:4067–73. https://doi.org/10.5897/AJAR2013.7096.Google Scholar
- 7.Yadessa E, Ebro A, Fita L, Asefa G. Livestock feed production and feed balance in Meta-Robi District, West Shewa Zone, Oromiya Regional State, Ethiopia. Aca Res J Agric Sci Res. 2016;4:45–54. https://doi.org/10.14662/ARJASR2016.072.Google Scholar
- 8.Hassen A, Ebro A, Kurtu M, Treydte AC. Livestock feed resources utilization and management as influenced by altitude in the Central Highlands of Ethiopia. Livest Res Rural Dev. 2010;22:1–19.Google Scholar
- 9.Wondatir Z, Mekasha Y, Wouters B. Assessment of productive and reproductive performance of dairy cattle nexus with feed availability in selected peri-urban areas of Ethiopia. J Cell Anim Biol. 2011;5:308–15. https://doi.org/10.5897/JCAB11.037.Google Scholar
- 10.Kassa H, Gibbon D, Tamir B. Use of livestock feed balance as a potential indicator of sustainability of tropical smallholder mixed farms—prevailing knowledge gaps: a case study from the Harar highlands of eastern Ethiopia. J Sustain Agric Lond. 2003;22:37–41.Google Scholar
- 11.Amsalu T, Addisu S. Assessment of grazing land and livestock feed balance in Gummara-Rib watershed, Ethiopia. Curr Agric Res J. 2014;2:114–22. https://doi.org/10.12944/CARJ.2.2.08.CrossRefGoogle Scholar
- 12.Tegene N, Dinku G, Mohammed B. Assessment of potential of natural pasture and other feed resources in sweet potato production system of Shebedino District, Sidama Zone, SNNPRS, Ethiopia. Int J Livest Prod. 2015;6:91–8. https://doi.org/10.5897/ijlp2015.0264.CrossRefGoogle Scholar
- 13.Molla A. Farmers’ knowledge helps develop site specific fertilizer rate recommendations, central highlands of Ethiopia. World Appl Sci J. 2013;22:555–63. https://doi.org/10.5829/idosi.wasj.2013.22.04.1196.Google Scholar
- 14.Amsalu A, Stroosnijder L, Graaff JD. Long-term dynamics in land resource use and the driving forces in the Beressa watershed, highlands of Ethiopia. J Environ Manag. 2007;83:448–59. https://doi.org/10.1016/j.jenvman.2006.04.010.CrossRefGoogle Scholar
- 15.Bekele M, Mengistu A, Tamir B. Livestock and feed water productivity in the mixed crop–livestock system. Animal. 2017;11:1852–60. https://doi.org/10.1017/S1751731117000416.CrossRefPubMedGoogle Scholar
- 16.Faul F, Erdfelder E, Buchner A, Lang A-G. G * Power 3: a flexible statistical power analysis program for the social, behavioral, and biomedical sciences. Behav Res Methods. 2007;39:175–91.CrossRefPubMedGoogle Scholar
- 17.Alam M, Sumy SA, Parh YA. Selection of the samples with probability proportional to size. Sci J Appl Math Stat. 2015;3:230–3. https://doi.org/10.11648/j.sjams.20150305.13.CrossRefGoogle Scholar
- 18.Kossila V. The availability of crop residues in developing countries in relation to livestock populations. In: Reed JD, Capper BS, Neate PJH, editors. Proceedings of plant breeding and the nutritive value of crop residues, 7–10 December 1987. Addis Ababa, Ethiopia: International Livestock Centre for Africa (ILCA); 1988. p. 29–39.Google Scholar
- 19.Tolera A, Said A. Prospects for integrating food and feed production in Welayita Sodo, Ethiopia. In: Stares JES, Said AN, Kategile JA, editors. The complementarity of feed resources for animal production in Africa. Proceedings of the joint feed resources networks workshop held in Gaborone, Botswana, 4–8 March 1991. Addis Ababa, Ethiopia: ILCA (International Livestock Centre for Africa); 1992. p. 309–18.Google Scholar
- 20.Food and Agriculture Organization of the United Nations (FAO). Master Land Use Plan, Ethiopian Range Livestock Consultancy Technical Report, AG/ETH/82/020/FAO. Rome, Italy; 1987.Google Scholar
- 21.Woody Biomass Inventory and Strategic Planning Project (WBISPP). A strategic plan for the sustainable development, conservation, and management of the woody biomass resources. Amhara Regional State, Final report. Addis Ababa, Ethiopia; 2002.Google Scholar
- 22.Ministry of Agriculture Fisheries and Food (MAFF). Energy allowances and feeding systems for ruminants. Reference Book 413. HMSO, London, UK; 1984. p. 85.Google Scholar
- 23.Church D, Pond W. Basic animal nutrition and feeding. New York: Wiley; 1982.Google Scholar
- 24.International Livestock Research Institute (ILRI). Feed Assessment Tool (FEAST) individual farmer interview questionnaire [Internet]. Nairobi, Kenya: ILRI; 2014. p. 21. https://www.ilri.org/feastmethodology. Accessed 27 Dec 2014.
- 25.Jahnke HE. Livestock production systems and livestock development in Tropical Africa. Kiel: Kieler Wissenschaftsverlag Vauk; 1982.Google Scholar
- 26.Kearl LC. Nutrient requirements of ruminants in developing countries. Logan: Utah State University; 1982.Google Scholar
- 27.International Business Machines Corporation (IBM Corp. Released). IBM SPSS Statistics for Windows, Version 23.0. Armonk, NY, USA: IBM Corp.; 2015.Google Scholar
- 28.Central Statistical Agency of the Federal Democratic Republic of Ethiopia (CSA). Agricultural sample survey in 2015/2016. Report on land utilization (private peasant holdings, Meher season). Addis Ababa, Ethiopia; 2016.Google Scholar
- 29.Blümmel M, Samad M, Singh OP, Amede T. Opportunities and limitations of food–feed crops for livestock feeding and implications for livestock–water productivity. Rangel J. 2009;31:207–12. https://doi.org/10.1071/rj09005.CrossRefGoogle Scholar
- 30.Haileslassie A, Peden D, Gebreselassie S, Amede T, Wagnew A, Taddesse G. Livestock water productivity in the Blue Nile Basin: assessment of farm scale heterogeneity. Rangel J. 2009;31:213–22. https://doi.org/10.1071/RJ09006.CrossRefGoogle Scholar
- 31.Kebebe EG, Oosting SJ, Haileslassie A, Duncan AJ, de Boer IJM. Strategies for improving water use efficiency of livestock production in rain-fed systems. Animal. 2015;9:908–16. https://doi.org/10.1017/S1751731114003115.CrossRefPubMedGoogle Scholar
- 32.Mcdermott JJ, Staal SJ, Freeman HA, Herrero M, Van de Steeg JA, Van De Steeg JA. Sustaining intensification of smallholder livestock systems in the tropics. Livest Sci. 2010;130:95–109. https://doi.org/10.1016/j.livsci.2010.02.014.CrossRefGoogle Scholar
- 33.Bogale S, Melaku S, Yami A. Matching livestock systems with available feed resources in the Bale Highlands of Ethiopia. Outlook Agric. 2008;37:105–10. https://doi.org/10.5367/000000008784648960.CrossRefGoogle Scholar
- 34.Tolera A. Feed resources for producing export quality meat and livestock in Ethiopia: examples from selected Woredas in Oromia and SNNP regional states. Ethiopia: Addis Ababa; 2007.Google Scholar
- 35.Bogale S, Melaku S, Yami A. Potential use of crop residues as livestock feed resources under smallholder farmers conditions in Bale highlands of Ethiopia. Trop Subtrop Agroecosyst. 2008;8:107–14.Google Scholar
- 36.Duncan AJ, Bachewe F, Mekonnen K, Valbuena D, Rachier G, Lule D, et al. Crop residue allocation to livestock feed, soil improvement and other uses along a productivity gradient in Eastern Africa. Agric Ecosyst Environ. 2016;228:101–10. https://doi.org/10.1016/j.agee.2016.05.011.CrossRefGoogle Scholar
- 37.Asfaw MA. Livestock–water interactions: the case of Gumara watershed in the Upper Blue Nile Basin, Ethiopia. Ph.D. dissertation, Der Humboldt-Universität zu Berlin, Germany; 2013; p. 1–141.Google Scholar
- 38.Haileslassie A, Peden D, Gebreselassie S, Amede T, Descheemaeker K. Livestock water productivity in mixed crop–livestock farming systems of the Blue Nile basin: assessing variability and prospects for improvement. Agric Syst. 2009;102:33–40. https://doi.org/10.1016/j.agsy.2009.06.006.CrossRefGoogle Scholar
- 39.Hussen M, Kechero Y, Molla M. Availability, yield and utilization practices of livestock feed resources in Gilgel Gibe catchments of Jimma Zone, Southwestern Ethiopia. Glob Vet. 2016;17:78–94. https://doi.org/10.5829/idosi.gv.2016.17.01.1046.Google Scholar
- 40.Tschopp R, Aseffa A, Schelling E, Zinsstag J. Farmers’ perceptions of livestock, agriculture, and natural resources in the rural Ethiopian highlands. Mt Res Dev. 2010;4:381–90. https://doi.org/10.1659/MRD-JOURNAL-D-09-00072.1.CrossRefGoogle Scholar
- 41.Sharma K, Pattanaik AK, Anandan S, Blümmel M. Food-feed crops research: a synthesis. Anim Nutr Feed Technol. 2010;10S:1–10.Google Scholar
- 42.Food and Agriculture Organization of the United Nations (FAO). Conducting national feed assessments—FAO animal production and health manual no. 15. Coughenour MB, Makkar HPS, editors. Rome: FAO; 2012.Google Scholar
- 43.Wondatir Z, Mekasha Y. Feed resources availability and livestock production in the central rift valley of Ethiopia. Int J Livest Prod. 2014;5:30–5. https://doi.org/10.5897/IJLP2013.0158.CrossRefGoogle Scholar
- 44.Yisehak K, Janssens GPJ. The impacts of imbalances of feed supply and requirement on productivity of free-ranging tropical livestock units: links of multiple factors. Afr J Basic Appl Sci. 2014;6:187–97. https://doi.org/10.5829/idosi.ajbas.2014.6.6.9168.Google Scholar
- 45.Moore AD, Bell LW, Revell DK. Feed gaps in mixed-farming systems: insights from the Grain and Graze program. Anim Prod Sci. 2009;49:736–48. https://doi.org/10.1071/AN09010.CrossRefGoogle Scholar
- 46.Abegaz A, Van Keulen H, Oosting SJ. Feed resources, livestock production and soil carbon dynamics in Teghane, Northern Highlands of Ethiopia Teghane, Northern Highlands of Ethiopia. Agric Syst. 2007;94(94):391–404. https://doi.org/10.1016/j.agsy.2006.11.001.CrossRefGoogle Scholar
- 47.Valbuena D, Tui SHK, Erenstein O, Teufel N, Duncan A, Abdoulaye T, et al. Identifying determinants, pressures and trade-offs of crop residue use in mixed smallholder farms in Sub-Saharan Africa and South Asia. Agric Syst. 2015;134:107–18. https://doi.org/10.1016/j.agsy.2014.05.013.CrossRefGoogle Scholar
- 48.Lenne JM, Fernandez-Rivera S, Blümmel M. Approaches to improve the utilization of food-feed crops-synthesis. Food Crop Res. 2003;84:213–22. https://doi.org/10.1016/s0378-4290(03)00152-7.CrossRefGoogle Scholar
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