3.1. Sources of Major Livestock Feed
The major feed resources in the study areas were natural pasture, crop residue, stubble grazing, agricultural byproducts, and forage crops, in descending order as ranked by respondents (Table 1), which is consistent with the reports of [10–12]. Natural pasture and crop residues were the primary and secondary sources of feed for livestock in all agroecologies (Table 1), as was the case in the majority of developing countries [13]. Furthermore, respondents and key informants reported that locally brewed byproducts were also used as a supplementary feed resource in the area.
Table 1
Ranked feed resources by Henry ranking methods
Agroecology | | Feed resources | |
Natural pasture | Crop residues | Stubble grazing | Agro-industrial byproduct | Forage crops |
Highland | Score | 85.0 | 76.8 | 68.0 | 14.8 | 60.0 |
Rank | 1 | 2 | 3 | 5 | 4 |
Midland | Score | 82.3 | 79.5 | 68.0 | 62.0 | 60.0 |
Rank | 1 | 2 | 3 | 4 | 5 |
Lowland | Score | 85.0 | 82.3 | 68.0 | 63.0 | 59.0 |
Rank | 1 | 2 | 3 | 4 | 5 |
Overall | Score | 85.0 | 74.0 | 68.0 | 63.0 | 59.0 |
Rank | 1 | 2 | 3 | 4 | 5 |
3.2. Grazing Lands Owned by Individuals
The percentage of households with private grazing lands was 44.2%, which was significantly higher in highland than midland and lowland agroecologies. This could be due to the lower forage production and smaller size of communal grazing land in highland agroecologies. According to Table 2, the total percentage of respondents who managed private grazing land was low. Nobody introduced improved forage in all agroecologies on private grazing lands, indicating a lack of farmer awareness of the benefits of improved forage and a limited supply of skilled extension services in the study areas. However, manure and fertilizer application, as well as invasive weed control, performed much better than other private grazing land management practices across all agroecologies (Table 2), despite no significant (p > 0.05) differences in private grazing land management practices across agroecologies.
Table 2
Private grazing land management techniques
Agroecology | Highland | Midland | Lowland | Overall | P value |
Respondents (%) had private grazing land | 21.1a | 16.8b | 6.3c | 44.2 | 0.006 |
Manure Application | 6.3a | 8.4 a | 3.2 a | 17.9 | 0.556 |
Weed control | 6.3 a | 7.4 a | 3.2 a | 16.8 | 0.613 |
Improved forages | 0.0a | 0.0a | 0.0a | 0.0 | 0.00 |
Fertilizer application | 8.4 a | 5.3 a | 2.1 a | 15.8 | 0.207 |
Irrigation | 1.1a | 0.0 a | 0.0 a | 1.1 | 0.387 |
Superscript letters with different values within the same rows are significantly different (P < 0.05 among agroecologies
3.3. Forage Crop Species
Chamaecytisus palmensis, Sesbania sesban, Vicia da scarpa, Pennisetum purpureum, Avena sativa, Chloris Guyana, and Pennisetum pedicellatum are among the forage crops that have been introduced (Table 3). These improved forage crops are widely used in various parts of the Amhara region [10, 14, 15]. According to respondents and direct observations, Chamaecytisus palmensis (tree lucerne) was the only forage in the highland areas, and it was significantly (P < 0.05) higher than in the midland and lowland agroecologies, which was consistent with the report [14]. This could be due to the lack of other improved species that have adapted to cold environmental conditions.
The diversity of forage crops was greater in the midlands than in highland and lowland agroecologies (Table 3). This could be due to a lack of forage species adapted to high moisture and high temperatures in highlands and lowlands agroecologies [16]. Furthermore, in highland and midland agroecologies, the percentage of respondents with Vicia dasycarpa and Sesbaina sesban was significantly lower (p < 0.05). Thus, the intervention of forage species that adapt to highland and lowland areas may necessarily require an increase in livestock production. The proportion of respondents with Pennisetum purpureum, Avena sativa, Chloris Guyana, and Pennisetum pedicellatum did not differ significantly (p > 0.05) across agroecologies.
Table 3
Percentage of respondents who had forage crops
| | AgroEcology |
| Highland | Midland | Lowland | Overall | P value |
Farmers (%) sown/planted improved forage | 17.7a | 27.1a | 4.2b | 49.0 | 0.000 |
Types of improved forages | | | | | |
Chamaecytisus palmensis | 17.7 a | 1.0b | 0.0 b | 18.8 | 0.000 |
Sesbania sesban | 0.0b | 25.0a | 3.1b | 28.1 | 0.000 |
Pennisetum purpureum | 0.0 a | 1.0a | 2.1a | 3.1 | 0.237 |
Chloris gayana | 0.0a | 4.2a | 2.1 a | 6.3 | 0.165 |
Avena sativa | 0.0a | 2.1a | 0.0a | 2.1 | 0.196 |
Vicia dasycarpa | 0.0b | 5.2a | 0.0b | 5.2 | 0.015 |
Pennisetum pedicellatum | 0.0a | 2.1a | 0.0a | 2.1 | 0.196 |
Means within the same row with different superscripts are significantly varied (P < 0.05) among agroecologies
3.4. Strategies for Forage Crop Development in the Study Areas
Backyard development was the most common forage crop strategy across all agroecologies, and it was significantly more common (P < 0.05) in highland and midland than lowland agroecologies, which was consistent with the observations [15]. This might be the case because backyard methods only required a limited amount of land around the homestead areas and did not compete with the production of food crops. However, none of the respondents in all agroecologies sowed or planted improved forage crops with food crops (Table 4). This indicated farmers' poor level of understanding of the value of improved forage strategies and the lack of knowledgeable extension services in the study areas. Farmers can increase the availability of high-quality animal feed, strengthen the important relationship between livestock and crop production, improve water and soil conservation, and reduce the amount of barren grazing lands by developing forage crops [7].
Table 4
Percent of respondents implementing forage crop production strategies
Agroecologies | | Improved forage development strategies | |
Backyard | Intercrop/under sowing | Forage strips | Stock exclusion | Alley cropping |
Highland | 16.7a | 0.0a | 0.0a | 0.0a | 0.0 a |
Midland | 25.0a | 0.0a | 3.1a | 1.0a | 0.0a |
Lowland | 3.1b | 0.0a | 0.0a | 0.00a | 2.1a |
Overall | 44.8 | 0.0 | 3.1 | 1.0 | 2.1 |
p value | 0.000 | 0.000 | 0.085 | 0.447 | 0.064 |
Means within the same column with different superscripts are significantly varied (P < 0.05) among agroecologies
3.5. Challenges to Forage Crop Production
In line with the reports of [14], the findings revealed that the majority (51.0%) of respondents in the study areas did not participate in the production of forage crops. This was caused by a lack of land, awareness of the problem, a lack of seeds, and farmers' concern as a result of birds being fed by farmers' crops as feeders (Table 5), which is consistent with the findings of previous studies[14, 17]. The lack of available land was the primary impediment to the cultivation of forage crops, and it was significantly (P < 0.05) higher in highland agroecologies than in midland and lowland agroecologies, supporting reports from the Hadiya zone [2, 14, 17, 18]. The reason for this could be that farmers prioritized growing food crops on the available areas rather than raising animal feed. This poor practice of forage development might be challenged by information and technology limitations. As concluded from group discussions, farmers in the study area prefer to grow food crops rather than feed on land because there are no comparative findings on the profitability of crop production and livestock production per unit of land.
The respondents also mentioned farmer awareness as an obstacle to the cultivation of improved forages, and there was no difference in agroecologies that was statistically significant (P > 0.05). In line with the findings of studies by [14, 18], farmers in the study areas lacked a thorough understanding of the systems for producing and utilizing enhanced forage crops. Due to a lack of awareness, farmers did not sow forage crops under terraces, borders, or intercropping. A lack of seeds and planting materials for suitable forage crop species also hampered forage crop production (Table 5), which was consistent with the findings of [14, 17]. The lack of forage species that are adaptive, particularly for highland agroecologies, is a significant limiting issue in the production of improved forages, according to the development agents and farmers who were interviewed. Because of the lack of farmers and organizations in various regions producing improved forage seeds, there is a restricted supply of seed and planting materials appropriate for the various agroecologies and development strategies. However, according to respondents, the peasant association, and district experts, the opportunities for the production of forage crops were rising consumer demand for animal products, expensive feed, crop-dominated areas for intercropping, seasonal fallow land, suitable agroecologies, increased soil erosion, and protection from climate change.
Table 5
Challenges of forage crop production in the study areas
| | Constraints of forage production | |
Agroecologies | Land shortage | Lack of awareness | lack of seed and planting materials | Fear of farmers birds set on forages | water shortage | Lack of capital to purchase seeds |
Highland | 26.0a | 8.3a | 5.2a | 3.1a | 2.1a | 2.1a |
Midland | 16.7b | 7.0a | 4.2a | 0.0a | 2.1a | 1.0a |
Lowland | 17.7b | 12.5a | 5.2a | 0.0a | 4.2a | 0.0a |
Total | 60.4 | 24.0 | 14.6 | 3.1 | 8.3 | 3.1 |
p value | 0.018 | 0.062 | 0.643 | 0.052 | 0.312 | 0.407 |
Percentages within the same column with different superscript letters are significantly varied (P < 0.05) across Agroecologies