ASSESSMENT OF EXISTING AGROFORESTRY PRACTICES IN WEST HARARGHE ZONE OF OROMIA REGION, ETHIOPIAAlemayehu Diriba 1, Shimelis
Dekeba 1, Wasihun Gizaw 1 1 Mechara Agricultural Research Center, Mechara, Ethiopia, P.O. Box 19, Mechara and Oromia Agriculture Research Institute, P.O. Box 81265, Addis Ababa, Ethiopia. |
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Received 5 November2021 Accepted 15 December2021 Published 31 December2021 Corresponding Author Alemayehu
Diriba, alemayhudiriba@gmail.com DOI 10.29121/granthaalayah.v9.i12.2021.4436 Funding:
This
research received no specific grant from any funding agency in the public,
commercial, or not-for-profit sectors. Copyright:
© 2021
The Author(s). This is an open access article distributed under the terms of
the Creative Commons Attribution License, which permits unrestricted use, distribution,
and reproduction in any medium, provided the original author and source are
credited. |
ABSTRACT |
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A study
was conducted in west Hararghe zone, on three districts, in six peasant
associations with the intention to identify and assess potentials,
constraints, opportunities and farmers’ perception on the existing
agro-forestry practice of the study area. The study was multistage sampling
method which 121 households were selected using random sampling technique.
Qualitative data was generated by conducting household survey interview,
focus group discussion, key informant interview, and direct field observation
order to fit intention of the study. The collected Data was manipulated using
suitable analytical software packages (SPSS, V.20) to calculate percentage
and frequency of events through descriptive statistics. Based on the
respondent’s idea across the districts, an average value of home garden
agroforestry practices with 86% increasing and 11.5% decreasing and 2.5% no
change trends were observed, while alley cropping of agroforestry practice
during the past ten years ago with 89.3% increasing and 10.7% decreasing
trend was observed (Table 4).
Almost all in both Hararghe zones; alley cropping system is the most familiar
than other existing agroforestry practices. For instance, an average value
across the districts, Kchat plantation in alley cropping practice during the
past ten years ago with 97.5% increasing and 2.5% decreasing trend was
recorded (Table 4). In
the result, the three top and the highest percentage observation of woody
species have been retaining and planting in farmland across districts with
the specific uses were Catha Edulis with (64.2%), Coffea with (49.9%) and
Cordia Africana with (36.7%) could be observed (Table 2). The
three top constraints of agroforestry practices were shortage of farmland
with (43.8%), lack of understanding with (24.8%) and nutrient competition
with (20.7%) observed. Basically, agroforestry practices need optimum
farmland size with related extent in order to compensate the observed
constraints. On the contrary, the three top opportunities of agroforestry
practices were Multipurpose Utilities with (26.1%), provision of shading with
(14.3%) and Climate Balance with (6.7%) observed. It was also found that
multipurpose trees shrubs play various traditional roles to local community.
Generally, retention and planting of trees/shrubs in farmlands are used for
fuel, construction, food, medicine, folder, and aesthetic value, shading
values, windbreak, soil conservation and soil fertility improvement, bee
forage and other uses in advance. |
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Keywords: Existing
Agroforestry Practices, Multidimensional Utilizes of Trees/Shrubs, Woody
Species 1. INTRODUCTION Agroforestry is
defining as “an ecologically based natural resource management system that
integration of tree with (fiber, food and energy), crop and/or animal on the
same land units, while maintaining ecosystem service”. |
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ICRAF (2000), ICRAF (2006). Worldwide deem that agroforestry give various ecosystem services through providing diversification of household need in addition to cultural service such as agro-tourisms, aesthetic values, demonstrations and educations. Principally, agroforestry affords amendable services such as soil conservation, watershed management, pest control and carbons sink. In so doing that, it gives higher contribution to the mitigation of global climate change Jose and Bardhan (2012).
In developing country especially Africa, rapid population growth, decline in per capita food production and environmental degradation are the main problems. Consequently, the need for intensification of agricultural productions coupled with population growth. Then the farmer force to expand the cultivation to hilly and marginal area Asfaw and Ågren (2007). This result aggravates the degradation and unsustainability of natural resource. In relation to this, agroforestry practice can be the only option to condense pressure on leftover natural forest as off deforestation and sustain biodiversity Kang and Akinnifesib (2000), Gustavo et al. (2004).
The tropical region has many traditional agroforestry practices such as scattered tree on crop field, homestead tree planting and multistory home garden Nair (1993). There are three common classification of agroforestry system (forms, structures and arrangements). Under the forms of agroforestry system classification are agro-silvo-cultural (crops + trees), silvo-pasture (trees + animals) and agro-silvo-pastoral (crop + trees + animals) systems Nair (1985). Under the structure of agroforestry system classification are crops under tree cover and multi-strata agroforestry. Under the arrangement of agroforestry system classifications are animal agroforestry, sequential agroforestry and minor agroforestry technique. Agroforestry practice in the tropic and sub-tropic is probably as old as agriculture itself Torquebiau (2000), McNeely and Schroth (2006).
In Ethiopia, the integration of tree and shrub into agriculture emerged many years ago (Edmond et al. 2000). In ancient time, the cultivation of domesticated and wild fruit tree was concentrated in monasteries and isolated churches as major source of food for the nuns, monks, hermits and warriors Gustavo et al. (2004). The historical development of agriculture in the country monitored the human expenditure time past and therefore much elder in northern Ethiopia than other parts. Numerous agroforestry systems are practiced in diverse part of the country. One of the first-born native agroforestry systems is the preservation of scattered trees (Faidherbia albida) on farmland of rift valley and highland of eastern Ethiopia. Example: farmers of southern Ethiopia preserve Cordia africana and Millettia ferruginea for upholding soil fertility on Enset-coffee based agroforestry isometrics Abebe (2005), Asfaw and Ågren (2007) . Coffee in agroforestry system can be referred as a good example in the Arsi zone Gololcha and Shenen Kolu districts, which are cultured under the shade of vestige native trees, such as Cordia africana, Erythrina abyssinica and Acacia abyssinica Alemayehu et al. (2017).
Most part of Ethiopian arable land is degraded because of soil erosion dominance. This might be due to no vegetation cover and topography of area thus usually prone to soil erosion. Therefore, agroforestry is the only solutions to reverse the situation in order to meet the multiple demands of forest and tree in sustain form to safe the remaining forest resource and renovate land degradation. Generally, integration of trees into the farm has to be adapted as biological soil and water conservation for livelihood diversification to meet multiple demands of farmer through agro-forestry practice thereby to mitigate global climate change Pandey (2002).
Now a day to resilience global climate changes that implementation of the desire agroforestry practices is to be as a mono option. So, assessment of traditional information of indigenous people is significant. Understanding of the prevailing agriculture scheme is the starting point for development of farming system. The intervention of agricultural development, in the past failed because of giving insufficient consideration to traditional information Miller and Nair (2006). Therefore, the recommended agroforestry practices have to be informed on the way for researchers, farmers and policymakers to understand the effectiveness of the trees/shrubs on the existing agroforestry practices. Even though the study could be implemented in west Hararghe zone on three districts; would not provide adequate information with evenly understanding of traditional agroforestry practices.
There are several customary agroforestry practices in different agro-ecological region of west Hararghe zone, but they are not well studied and documented based on the report of Yusuf et al. (2020). Assessing of information as well as identifying of constraint and opportunity on the existing agroforestry practices is essential for agroforestry research and advance work in the study areas. In so doing that the study aimed to assess the indigenous agro-forestry practice in the study area and to highlight opportunities and constraints of the agro-forestry practice for sustainable agricultural production alternatively. Furthermore, to assess potential of agro-forestry practices through examining the existing practices with the context of identifying the best practices in the farming system providing to be positive harmony for similar agroecology of the study area.
1.1. GENERAL OBJECTIVE
To assess the existing agroforestry practices in West Hararghe Zone, Oromia Region, Ethiopia.
1.2. Specific objectives
· To assess and identify potentials, constraints, opportunities, perception of farmers as well as preference of tree /shrub species in the existing agro-forestry practices.
2. MATERIALS AND METHODS
2.1. Description of the study area
Oda Bultum woreda is found in West Hararghe Zone, Oromiya Regional State. It is located in the eastern part of the country, 362km from Addis Ababa and 37km from Chiro. Bedessa town serves as the main administrative center of Oda Bultum woreda. Livelihood of woreda based on rain-fed and mixed farming system that constituting about 90%, and agro-pastoralism estimated at 10%. Maize, sorghum, teff, wheat and barley are the major food crops while chat, coffee and pepper are the most important cash crops. The mean annual rainfall is 950mm-1053mm, with maximum and minimum temperature is 28.820c and 12.510c, respectively.
Boke district is one of the districts of West Hararghe zone. The dominant cash crops are coffee and Kchat manufacture. It is situated at 391 km East of Addis Ababa and about 69 km south of Chiro that is capital town of west Hararghe zone. The district obtains an average annual rainfall of 850 mm and average temperature is 20°C. It shares borders with Chiro district in the west and north, Oda Bultum district in the south and Shenen dhugo district in the East. The district is found within 1300 to 2400 m above sea level. Similarly, Hancar district is one of the districts found in West Hararghe zone. It is situated in the eastern part of the country, 352km from Addis Ababa and about 100km from Chiro. Altitude range of Hancar district is 1400-3000m aslv. Mean annual rainfall is 800mmto 2000mm, and with maximum and minimum temperature of the district is about 29.50c and 100c, respectively (Oromia livelihood profile, 2006).
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Figure 1 Data of
average Temperature and annual mean Rainfall of Hancar, Odabultum and Boke
districts, 2020 |
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Figure 2 Map of
the study districts |
2.2. Selection of the Study Area
For the intended purpose, three districts, three kebele from each district and fourteen farmers from each kebele were selected to conduct the survey based on agro ecology and altitude range that from low land, mid land and highland of agro ecologies zones. The data was collected based on household survey carried out in districts of the West Hararghe zone in Oromia region, Ethiopia.
2.3. Sample procedure and sample
Size
The survey was carried out in Western Hararghe Zone. To select district and Kebele, a purposive sampling method was applied based on the objectives of the activity. Accordingly, three districts were selected purposefully based on their exposure to agro-forestry practices, having considerable diversity in terms of agro-ecological zones and their experiences of agro-forestry practices. Then, from each district, three kebele were chosen randomly, based on similar criteria as mentioned above. The farm households for interview were selected randomly from the sample kebele.
Finally, from each kebele of one district that fourteen farmers were selected randomly and a total of 121 households for the intended purpose. Fruit full data was collected from 121 households with semi-structured questionnaires concerning to consistent of agroforestry practice by individual farmers’ interview. The inquiry guide checklist was supplied for each individual and focus group discussions to capture the data from semi-structured questionnaires including farming characteristics of the study area, which are mainly serving in agroforestry practice.
2.4. Method of Data Collection
Semi-structured interviews from the selected individual farmers, focus group discussions and personal observations was implemented to generate primary data pertaining to the existing agro-forestry systems and practices in the study area. The survey from household was implemented to collect data on general socio-economic characteristics of sample households and to know facts about the household, their experience in agro-forestry practice, reasons for their participation in agro-forestry practices, indigenous knowledge on agroforestry practice and constraints and opportunities they faced.
The major source of data was gained from sample households and focus group discussions to get preliminary information about the agro-forestry practices, prevailing opportunities and constraints in implementing agro-forestry practices with key informants (DAs, community leaders), elders and experienced farmers by means of checklist and questions with the intention of explore information pertaining with agro-forestry practices in the study area.
2.5. The collected Data
The input of all inquiries from each individual and focus group checklists’ data/ feedback, including the plant species occurs that were mainly serving in agroforestry system, perception of farmers on agroforestry utilities, opportunities and constraints, and also the types of agroforestry practices in the study area were collected for further analysis.
2.6. Method of Data Analysis
The recorded data was coded and entered into the computer. Quantitative data was analyzed by using descriptive statistics such as frequency and percentages in order to describe the event as it was. On the other hand, qualitative data was analyzed through narration and description.
Finally, the available data was compiled using Statistical software (SPSS) version 20. Qualitative data that obtains from interview and discussion was analyzed and described through concepts and opinions, by sorting out, grouping and organizing in the field that to supplement the survey result. In general, the data was managed and analyzed by descriptive analysis and narration.
3. RESULT AND DISCUSSION
3.1. Characteristics of Household Samples
The result of this study indicated that the existing
agroforestry practices have been done by men due to cultural value of the
country. Thus, out of the total
respondents, 121 (96.3%) of them were male, while the rest 4 (3.3%) of them
were female. The survey result
showed that only 43% of the respondents were educated, while 57% were
uneducated. With regards to the experience of farming status that below 25 years of the respondents were 11.6%; while above 25
years of the respondents were 88.4% (Table 1).
This means that the respondents were native to the study area. The idea
reflected nativness of respondent was 98.3%; while 0.8% newcomers to the study
area. The eminences to main
problem of farmland were soil erosion, soil fertility, drought, disease and
water logging that with 13.2%, 33.1%, 28.1%, 11.6 % and 6.6 % observed,
respectively. The other standing points of main
problem of the respondents on
farming system were shortage of farmland
with 71.1%, capita with 8.3 %, labor with 2.5% and input problem with 16.5%
observed (Table 1). Agro ecological zone of the study areas is
high land of Hancar district with 33.1 % coverage, midland of Odabultum
district with 33.9% coverage and low land of Boke district with 33.1% coverage
perceived (Table 1).
Table 1 Descriptive Statistics of Socio-economic characteristics of the offenders |
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Variables |
Values |
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No |
Indicator |
Frequency |
Percentage (%) |
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1 |
Gender of household |
Male |
117 |
96.7 |
Female |
4 |
3.3 |
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Total |
121 |
100 |
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2 |
Education level of household |
Educated |
69 |
57 |
Un educated |
52 |
43 |
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|
Total |
121 |
100 |
|
3 |
Experience of farming system |
Below 25 years |
14 |
11.6 |
Above 25 years |
107 |
88.4 |
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Total |
121 |
100 |
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4 |
Presences |
Native |
119 |
98.3 |
Newcomers |
1 |
0.8 |
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Total |
121 |
100 |
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5 |
Main Problem of Farmland |
Soil erosion |
16 |
13.2 |
Soil fertility |
40 |
33.1 |
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Drought |
34 |
28.1 |
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Weed |
7 |
5.8 |
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Disease |
14 |
11.6 |
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Waterlogging |
8 |
6.6 |
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Total |
121 |
100 |
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6 |
Main Problem of Farming system |
Land size |
26 |
71.1 |
Capital |
10 |
8.3 |
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Labor |
3 |
2.5 |
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Input |
20 |
16.5 |
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Total |
121 |
100 |
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7 |
Respondents with Districts |
Hancar |
40 |
33.1 |
Odabultum |
41 |
33.9 |
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Boke |
40 |
33.1 |
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Total |
121 |
100 |
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8 |
Respondents with Agro ecological zone |
Lowland (<1500) |
40 |
33.1 |
Midland (1500-2300) |
41 |
33.9 |
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Total |
121 |
100 |
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Source: Survey Result, 2020/21 |
3.2. Reason of Farmer Implementing Agroforestry Practices
Small holder farmers in the study area have a great awareness about the benefit of traditional agroforestry practice. Most of the respondents believed that traditional agroforestry practices had a vital role to enhance the overall productivity of farmlands. The major reason and benefit of planting and retention of woody species in farmland as agroforestry practices in the study area used for household consumption, environmental services and ecological balance through multidimensional delivery. Additionally, the use and service of woody species in farmlands are as food, feed, fuel, income, construction, shade and soil fertility improvement. So, the farmers in the study area have been adapting diversified uses and services from retained and planted trees/shrubs species in their farmlands.
In the results, the three top and the highest percentage observation of woody species that have been retaining and planting in farmland across districts with the specific uses are Catha Edulis, Coffea and Cordia Africana (Table 2). The result of this study in line with the findings of Yusuf et al. (2020), that asserted trees/shrubs species were deliberately retained and/or planted in farmlands have served the people for supplying food, fodder, income generation, wood, shade and environmental services.
Generally, the study had reflected that smallholder farmers of western Hararghe zone have well perceived and identified the implementation and value of trees/shrubs species from the existing agroforestry practices. Thus, each of the tree/shrub species had own benefits to sustain livelihood of the societies.
Table 2 The Type of Trees/Shrubs and their uses in Agroforestry practices across districts |
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Districts |
Scientific name |
Local Name |
uses of trees/shrubs
for: |
Frqncy. |
(%.) |
Boke |
1-Catha Edulis |
Jima |
Chewing/Feed/Income/Fuel |
37 |
14.2 |
2- Coffea |
Buna |
Drinking/Income |
37 |
14.2 |
|
3- Cordia Africana |
Weddessa |
Shade/Timber/Income/Fuel |
28 |
10.7 |
|
4-
Mangifera Indica |
Maango |
Food/Income/Shade |
24 |
9.2 |
|
5-Papaya |
Paapaayyaa |
Food/Income/Shade |
16 |
6.1 |
|
6-Moringa |
Shiferaw |
Food/Feed/Medicinal Plant |
12 |
4.6 |
|
7-Ficus Sycomorus |
Harbu |
Shade/Timber/Fuel |
11 |
4.2 |
|
8-Terminalia Brownie |
Berensa, |
Shade/Timber/Fuel |
11 |
4.2 |
|
9-Acaciaalbida |
Garbi |
Shade/Timber/Fuel |
10 |
3.8 |
|
10-Olia Africana |
Ejarsa |
Shade/Fuel |
9 |
3.4 |
|
11-Sesbania Sesban |
Enchini, Harcha |
Shade/Feed/Fuel |
9 |
3.4 |
|
12-Vernonia Amygdalina |
Ebicha |
Feed/Fuel/Medicinal Plant |
9 |
3.4 |
|
13-Ziziphus Mucronata |
Qurqura |
Shade/Feed/Fuel |
9 |
3.4 |
|
14-Shugerken |
Shankora |
Food/feed/Income |
7 |
2.7 |
|
15-Maesa Lanceolata |
Abayi |
Shade/Fuel |
6 |
2.3 |
|
16-Otostegia Integrifolia |
Tingiti |
Medicinal Plant |
6 |
2.3 |
|
17-Podocarpus Falcatus |
Bibirsaa |
Shade/Timber |
4 |
1.5 |
|
18-Melia Azedarach |
Muka Kinin |
Shade/Feed/Fuel |
3 |
1.1 |
|
19-Musa Acuminate |
Werqe |
Shade/Food/Feed |
3 |
1.1 |
|
20--Orange |
Birtukana |
Food/Shade |
3 |
1.1 |
|
21-Mimusops Kummel |
Mito |
Shade/Food/Fuel |
3 |
1.1 |
|
22-Sitress Limen |
Xuxxo |
Food/Shade |
2 |
0.8 |
|
23-Tamarindus Indica |
Roka |
Shade/Fuel |
2 |
0.8 |
|
Sub-total |
261 |
100 |
|||
Hancar |
1-Catha Edulis |
Jima |
Chewing/Feed/Income/Fuel |
50 |
20.4 |
2-Cordia Africana |
Waddesa |
Shade/Timber/Income/Fuel |
40 |
16.3 |
|
3-Coffea |
Buna |
Drinking/Income |
33 |
13.5 |
|
4-Acacia
albida |
Garbi |
Shade/Timber/Fuel |
30 |
12.2 |
|
5-Casimiroa Edulis |
Kasamiro |
Food/Shade/Fuel |
18 |
7.3 |
|
6-Mangifera Indica |
Maango |
Food/Income/Shade |
17 |
6.9 |
|
7- Caesarian Cunninghamiana |
Shewshawe |
Shade /Fuel |
10 |
4.1 |
|
8-Persea Americana |
Avocado |
Shade/Food/Fuel |
9 |
3.7 |
|
9- Shugerken |
shankora |
Food/feed/Income |
7 |
2.9 |
|
10-Albizia Schimpeiana |
Muka Arba |
Shade/Fuel |
6 |
2.4 |
|
11-Annona Senegalensis |
Komate,Gishxa |
Shade/Food/Fuel |
6 |
2.4 |
|
12-Casuarina Equisetifolia |
Shuwshuwe |
Shade/Timber/Fuel |
5 |
2 |
|
13-Combretum Molle |
Bika |
Shade/ Food/Feed/Fuel |
5 |
2 |
|
14-Acacia Senegal |
Saphensa, Garbi Dima |
Shade/Fuel |
3 |
1.2 |
|
15-Acacia Tortolis |
Tedecha |
Shade/Fuel |
2 |
0.8 |
|
16-Cactus |
Tinii |
Food/Feed |
2 |
0.8 |
|
17--Melia Azedarach |
Muka Kinin |
Shade/Feed/Fuel |
2 |
0.8 |
|
Sub-total |
245 |
100 |
|||
Odabultum |
1-Catha Edulis |
Jima |
Chewing/Feed/Income/Fuel |
90 |
29.6 |
2-Coffea |
Buna |
Drinking/Income |
59 |
19.4 |
|
3-- Cordia Africana |
Waddesa |
Shade/Timber/Income/Fuel |
38 |
12.5 |
|
4- Acacia albida |
Garbi |
Shade/Fuel |
30 |
9.9 |
|
5- Eucalyptus |
Bahargamo |
Constriction/Income/Fuel |
18 |
5.9 |
|
6--Gravilia Robusta |
Gravilia |
Shade/Timber/Income/Fuel |
18 |
5.9 |
|
7-Erythrina Abyssinica |
Walensu |
Shade/Feed/Fuel |
10 |
3.3 |
|
8--Juniperus Procera |
gaantra |
Shade/Timber/Fuel |
9 |
3 |
|
9-Balanites Aegyptiaca |
Bedena, Baddano |
Shade/Timber/Fuel |
8 |
2.6 |
|
10--Ehretia Cymosa |
Ulaga, |
Shade/Fuel |
6 |
2 |
|
11-Elephant Grass |
Shankora Hori |
Feed |
6 |
2 |
|
12-Croton Macrostachyus |
Bakanisa |
Shade/Fuel |
5 |
1.6 |
|
13-Mangifera Indica |
maango |
Food/Income/Shade |
2 |
0.7 |
|
14-Rhus Natalensis |
Debobosso |
Shade/Fuel |
2 |
0.7 |
|
15-Tamarindus Indica |
Roka |
Shade/Fuel |
2 |
0.7 |
|
16-Ziziphus Mucronata |
qurqura |
Shade/Feed/Fuel |
1 |
0.3 |
|
Sub-total |
304 |
100 |
|||
Grand Total |
810 |
100 |
3.3. Perception of farmers about Agroforestry
The current practices of smallholder farmers
on the existing agroforestry practices into their farm plots were recorded
through informant interviews. Of 121 respondents; 70 informants with (57.9%)
replied “strongly agree”; while
2 informants with (1.7%) replied “Neural “perception that “an agroforestry practice increase
farm income” (Table 3). So, the proportion of smallholder farmers
with a positive attitude to existing agroforestry practices on their farmland
is significantly higher than those who were not clearly and openly optimistic (Table 3). Similarly, 76 informants with 62.8%
replayed “agree”: that “agroforestry practices reduce the chance of completely
crop faille” (Table 3). This response reflected that agroforestry
practice help farmers to meet their basic need and minimize the risk of the
production system’s total failure. The result of this study in line with ICRAF (2006) that, Agroforestry practice has reduced the
probabilities of comprehensive crop disappointment. Based the respondent’s
idea; they had awareness and positive attitude based on a given arrogances
inquiry of the existing agroforestry practices (Table 3). Generally, the farmers had positive
perception on agroforestry practices in the study area and they know very well
on its utilities for income diversification, improvement of soil quality, fuel,
construction materials, food, and feed, provision of shade, accessibility and
ecological value etc, could be understood from the given inquiry parameters (Table 3).
Table 3 Perception of farmers on Existing Agroforestry Practices |
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Attitude of respondents to Agroforestry practices |
Perception value of respondents across district |
||||||||||
Degree of perception |
Ancar |
Odabultum |
Boke |
Grand Total |
|||||||
Frequency |
Per (%) |
Frequency |
Per (%) |
Frequency |
Per (%) |
Frequency |
Per (%) |
||||
1 |
Does an
agroforestry practice increase farm income |
-Strongly
Agree |
24 |
60 |
20 |
48.8 |
26 |
65 |
70 |
57.9 |
|
-Agree |
16 |
40 |
21 |
51.2 |
12 |
30 |
49 |
40.4 |
|||
-Neutral |
0 |
0 |
0 |
0 |
2 |
5 |
2 |
1.7 |
|||
-Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Strongly
Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
2 |
Does an
agroforestry practice improve soil fertility and soil and water conserve |
-Strongly
Agree |
4 |
10 |
20 |
48.8 |
17 |
42.5 |
41 |
33.8 |
|
-Agree |
1 |
2.5 |
17 |
41.5 |
22 |
55 |
40 |
33.0 |
|||
-Neutral |
15 |
37.5 |
2 |
4.9 |
0 |
0 |
17 |
14.1 |
|||
-Disagree |
19 |
47.5 |
1 |
2.4 |
1 |
2.5 |
21 |
17.5 |
|||
-Strongly
Disagree |
1 |
2.5 |
1 |
2.4 |
0 |
0 |
2 |
1.6 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
3 |
Does an
agroforestry practice reduce the chance of completely crop faille |
-Strongly
Agree |
14 |
35 |
9 |
22 |
15 |
37.5 |
38 |
31.5 |
|
-Agree |
26 |
65 |
27 |
65.9 |
23 |
57.5 |
76 |
62.8 |
|||
-Neutral |
0 |
0 |
5 |
12.2 |
2 |
5 |
7 |
5.7 |
|||
-Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Strongly
Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
4 |
Does
agroforestry practice save time on collecting fodder and fuel wood |
-Strongly
Agree |
5 |
12.5 |
9 |
22 |
15 |
37.5 |
29 |
24 |
|
-Agree |
30 |
75 |
27 |
65.9 |
20 |
50 |
77 |
63.6 |
|||
-Neutral |
1 |
2.5 |
5 |
12.2 |
2 |
5 |
8 |
6.6 |
|||
-Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Strongly
Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
5 |
Does an
agroforestry practice take a long time to get income |
-Strongly
Agree |
7 |
17.5 |
8 |
19.5 |
14 |
35 |
29 |
24 |
|
-Agree |
26 |
65 |
25 |
61 |
21 |
52.5 |
72 |
59.5 |
|||
-Neutral |
2 |
5 |
3 |
7.3 |
2 |
5 |
7 |
5.8 |
|||
-Disagree |
1 |
2.5 |
1 |
2.4 |
1 |
2.5 |
3 |
2.5 |
|||
-Strongly
Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
6 |
Does an
agroforestry practice maintain weather condition |
-Strongly
Agree |
18 |
45 |
13 |
31.7 |
17 |
42.5 |
48 |
39.7 |
|
-Agree |
22 |
55 |
22 |
53.7 |
18 |
45 |
62 |
51.2 |
|||
-Neutral |
0 |
0 |
1 |
2.4 |
1 |
2.5 |
2 |
1.6 |
|||
-Disagree |
0 |
0 |
1 |
2.4 |
1 |
2.5 |
2 |
1.6 |
|||
-Strongly
Disagree |
0 |
0 |
0 |
0 |
1 |
2.5 |
1 |
0.8 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
7 |
Does an agroforestry
practice sustain bio-diversities conservation |
-Strongly
Agree |
12 |
30 |
9 |
22 |
12 |
30 |
33 |
27.3 |
|
-Agree |
24 |
60 |
29 |
70.7 |
23 |
57.5 |
76 |
62.7 |
|||
-Neutral |
4 |
10 |
2 |
4.9 |
5 |
12.5 |
11 |
9.1 |
|||
-Disagree |
0 |
0 |
1 |
2.4 |
0 |
0 |
1 |
0.8 |
|||
-Strongly
Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
8 |
Does an
agroforestry practice sustain hydrologic cycling |
-Strongly
Agree |
13 |
32.5 |
11 |
26.8 |
15 |
37.5 |
39 |
32.3 |
|
-Agree |
20 |
50 |
22 |
53.7 |
21 |
52.5 |
63 |
52.1 |
|||
-Neutral |
3 |
7.5 |
5 |
12.2 |
2 |
5 |
10 |
8.2 |
|||
-Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Strongly
Disagree |
0 |
0 |
3 |
7.3 |
0 |
0 |
3 |
2.4 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
9 |
Does an
agroforestry practice the option to save deforestation |
-Strongly
Agree |
19 |
47.5 |
17 |
41.5 |
21 |
52.5 |
57 |
47.2 |
|
-Agree |
16 |
40 |
18 |
43.9 |
16 |
40 |
50 |
41.3 |
|||
-Neutral |
1 |
2.5 |
1 |
2.4 |
1 |
2.5 |
3 |
2.5 |
|||
-Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Strongly
Disagree |
0 |
0 |
1 |
2.4 |
0 |
0 |
1 |
0.8 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
10 |
Do you think
tree production in farm land minimize deforestation |
-Strongly
Agree |
34 |
85 |
33 |
80.5 |
34 |
85 |
101 |
83.5 |
|
-Agree |
3 |
7.5 |
5 |
12.2 |
3 |
7.5 |
11 |
9.1 |
|||
-Neutral |
3 |
7.5 |
3 |
7.3 |
3 |
7.5 |
9 |
7.4 |
|||
-Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Strongly
Disagree |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||
-Total |
40 |
100 |
41 |
100 |
40 |
100 |
121 |
100 |
|||
Source: Survey Result, 2020/21 |
|||||||||||
3.4. Trends of Agroforestry practices
The major
trends of agro forestry practice involved in the study area were identified (Table 4). Similar to other parts of Ethiopia, the
following existing agroforestry system and the special practices of the study
areas were identified. The effect of the study exposed that, among the
different existing traditional of agroforestry practices; the trend of parkland
agroforestry practice in the past 10 years duration across the districts was
indicated increasing scenario. So over all in average increasing with 83.5%,
decreasing with 12.4% and no change with 4.1% were recorded (Table 4).
Trend of home
garden agroforestry practice was observed in Hancar with 87.5% increasing, 5%
decreasing and 7.5% no change; whereas in Odabultum district 82,2% increasing,
17.5% decreasing and 0% no change, while 87.5% increasing, 12.5% decreasing and
5% no change was recorded in Boke district that with an average value of 86%
increasing and 11.5% decreasing observed (Table 4). Trends of alley cropping agroforestry
practice in Hancar inquired 97.5% increasing, 2.5% decreasing and 0% no change,
and in Odabultum district 82.9% increasing, 17.1% decreasing and 0% no change;
while in Boke district 87.5% increasing, 12.5% decreasing and 0% no change was
recorded and also with an average value was 89.3% increasing and 10.7%
decreasing was observed (Table 4). Almost all in both Hararghe zones; alley
cropping practice is the most familiar than other existing Agroforestry
practices. For instance, Trends of Kchat plantation in alley practice was 97.5%
increasing, 2.5% decreasing and 0% no change was recorded in Hancar district,
while 85.4% was increase, 14.6% decrease and no change was 0% recorded in
Odabultum district; whereas 92.5% was increasing, 7.5% was decreasing and 0%
was no change recorded in Boke district; and with an average value of districts
for Kchat plantation was 91.8% increasing, 8.2% was decreasing was observed (Table 4).
On the other
side, in alley practice; the trend of coffee plantation was contrary of Kchat
plantation across the district that means Kchat plantation is dominating and
replacing Coffee plantation almost in all Hararghe districts surprisingly (Table 4). However, it makes subjective imperfection
of human mind; Hararghe farmers are very sensitive to Kchat plantation for
their livelihood dependency thereby used for soil and water conservation purpose.
Generally, the
study result implies that domination of Kchat plantation across the districts
is increasing scenarios extremely.
Table 4 Trend values of Existing Agroforestry Practices across the districts in the past 10 years |
|
||||||||||||
Trend of Existing Agroforestry Practices in the last 10 years |
Trend value of respondents across district |
|
|||||||||||
Degree of Trends |
Hancar |
Odabultum |
Boke |
Grand total |
|||||||||
Freq uency |
Per (%) |
Freq uency |
Per (%) |
Freq uency |
Per (%) |
Freq uency |
Per (%) |
||||||
1 |
Trend of tree
planting in the last 10 years |
Increasing |
35 |
87.5 |
27 |
65.9 |
33 |
82.5 |
95 |
78.6 |
|||
Decreasing |
4 |
10 |
9 |
22 |
5 |
12.5 |
18 |
14.8 |
|||||