Research Article | | Peer-Reviewed

Factors Affecting Farmers’ Participation in Watershed Management Programs in Northern Ethiopia: A Case Study in the Upper Mugie Sub-watershed

Received: 19 May 2026     Accepted: 8 June 2026     Published: 29 June 2026
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Abstract

The purpose of this study was to evaluate the factors influencing farmers’ participation in watershed management in the Mugie Sub-watershed, located in the northeastern highlands of Ethiopia. A combination of purposive and random sampling techniques was used to select 200 households from four villages. Data was collected using a structured survey questionnaire, focus group discussions, and key informant interviews. The data were analyzed using a range of statistical techniques, including descriptive statistics, Pearson correlation, and regression analysis. The results revealed that farmers’ perception was strongly correlated (r = 0.612, p < 0.01) with their decision to participate in watershed management programs, followed by stakeholders’ support (r = 0.163, p < 0.05). In contrast, the slope of the farmland and the gender of the household head showed significant negative associations. Binary logistic regression analysis further indicated that six independent variables were important in explaining farmers’ decisions to participate in watershed management programs. These variables included land redistribution, gender, family labor force, educational opportunity, farm size, and land slope. Land redistribution, gender, family labor force, educational opportunity, and land slope had negative effects, whereas farm size had a positive effect. Further analysis also demonstrated the role of individual variables in explaining variation in farmers’ decisions to participate in the program. Among these, two variables were found to be statistically significant: the gender of the household head and land tenure security. Accordingly, the chi-square value for gender (X2 = 9.052) was statistically significant at the 95% confidence level. Similarly, the chi-square value for land tenure security (X2 = 8.691) was also statistically significant at the 95% confidence level. The findings of the study suggest the need to raise farmers’ awareness of the long-term benefits of watershed management programs and to design strategies that help diversify their livelihoods.

Published in International Journal of Environmental Protection and Policy (Volume 14, Issue 3)
DOI 10.11648/j.ijepp.20261403.12
Page(s) 71-83
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2026. Published by Science Publishing Group

Keywords

Binary Logistic Regression Model, Ethiopia, Farmer, Participation, Watershed Management

1. Introduction
Drainage basin worldwide look adding force from ground retrogression, slumping water quality, and decreased ecosystem services. Incorporated Drainage basin management embraces water potential use scheduling, defilement prevention, and confirmable growing furnishes an efficient framework for overcoming these obstacles . Even though, the success of drainage basin platform always based on the agreement of local communities to take part, and uncertainty in such inclusion comes a main dispute.
In Ethiopia, where farming yields close to 42% of GDP and utilizes greater than 80% of the population , drainage basin retrogression occurs a sever endanger to farming economic and local living. The Ethiopian highlands are highly influenced by land wearing, decreasing productivity, and deforestation . These obstacles are expanded by erratic rainwater, rugged topography, and greater population and living concentration . As an outcome, silt supplies in main large natural stream accomplish 180–900 t year-1 km-2 , and edge of large natural stream carry an around 1.3 billion tons of silt yearly . Land retrogression thus stays a major obstacle to farm growth and economic evolution .
Legal drainage basin management openings in Ethiopia started in the 1970s, but too soon interferences principally relied on top-down soil and water preservation (SWP) platforms that defined technical construction with a few community take part . Even though these interferences decreased land wearing, they could not made combination with confirmable land management and living constituents . Realizing these outcomes, Ethiopia follow community-based, collaborated drainage basin growing resembles in the too soon 2000s to good preservations with local social and ecologic facts .
Other than these displacements, drainage basin results stay variable crosswise areas. In the Amhara Region, ground retrogression shows in the deprivation of 2–4 billion tons of soil yearly and rendition 20,000–30,000 ha ungenerative . The Simada District—home to the Upper Mugie sub-watershed is one of the most retrograded, exercising danger wearing, drought, and reducing generativity. Many drainage basin projects have been put through, yet their sustainability differ due to various social and biophysical situations, spotlighting the demand for context-particular participatory designing.
Former studies have emphasized that husbandman participation in drainage basin growing is affected by different personal, physical, and institutional factors. These let in demographic variables such as age, sex, and family size ; education and mindfulness ; former taking part in maturation planes ; and making close interaction with propagation stakeholders and focal persons . Other researches shows that socioeconomic variables, such as financial gain and working class existence, influence inclusivment in protection tasks , while physical factors like ground size, ground tenure protection, and incline also affect taking part. Mindfulness of resource degradation likewise maneuvers a crucial function . Findings result on the effect of age is fused .
Having that farmers’ taking part is a core to the conformability of drainage basin startups, separating the factors directing inclusivement is vital for planning efficient platforms tailored to rural socio-ecological perspectives . This finding therefore investigates the personal, physical, and institutional constraints of husbandman’s taking part in drainage basin management platforms in the Upper Mugie sub-watershed of Northern Ethiopia.
2. Methodology
2.1. Description of the Study Area
Geographically, upper Mugie sub-watershed is found at 11.42-degree E, 38.25-degree N and 2472 meters above mean sea level (AMSL). Administratively, it is situated in Simada districts, South Gondar Zone, Amhara Regional State (Figure 1). The sub-watershed is situated just 777 km North of Addis Ababa (the capital city). It masks a total area of 152 km2. The detailed critical inspection filed is qualified by various topographic stipulations. A mountainous and highly dissected landscape with immerse side qualified many portion of the sub-watershed. The ground is with deficit of wealth in the sub-watershed due to greater population pressing and degradation.
The meteorological data of the work was gained from Debretabor Meteorological Station. Geographically, Debretabor Meteorological Station is found at 11.51-degree E, 38.10-degree N and 2706 meters above mean sea level (AMSL). The study area has the mean minimum and mean maximum temperature of 7.5°C and 24.9°C, respectively. The monthly mean minimum temperature varied from 7.5°C in December to 10.9°C in April (Figure 3). The monthly mean maximum temperature varied from 19.1°C in July to 24.9°C in March (Figure 3).
The drainage basin gets 1492.4 mm average rainwater yearly. The monthly modal values for 26 Years (1997-2022) of Climatic Deberetabor Station were gathered from the National Meteorological Agency (Figure 2). Generally, the rainfalls of the watershed area were described by its high variability in distributions. Meher or Kiremt rainfall is largely gained in the four months (from June to September).
Figure 1. Location map of the study area.
Figure 2. Monthly rainfall, (1997-2022).
Figure 3. Monthly average maximum (Tmax) and minimum (Tmin) temperature.
2.2. Methods of Data Collection and Sampling
Both primary and secondary data sources are used for this study. The primary data lets in household survey questionnaire, focus group discussions (FGDs), field observations, and key informant interviews. Secondary data were also collected from former researches, studies, records, journals, and cyberspace root ages. The household survey questionnaire was done to collect data about demographic and socioeconomic characteristics of sample households, institutional services, biophysical characteristics, plot level characteristics, and various sustainable land management (SLM) activities taken by farmers of the study area. The questions were both closed-ended and open ended types. Accordingly, the survey questionnaire was conducted between December and January 2017. A formal survey instrument was prepared, and trained enumerators gathered the data from the families through personal interviews. This time was selected mostly to prevent interference of farmers’ farming tasks. Thus, it is simple to interview the sample farm house holds and gather the postulated data. The constructed household questionnaire was pre-tested as a pilot survey in the selected villages before full execution. The pilot survey enhances that the current questionnaire is relevant and purposeful to the modal answerer, and to assure which questions were relevant for the purpose of the study. Hence necessary modifications were made standing from the feedback gained from the pre-test. Data on the farmers’ sensing of land degradation, farming productivity, and effectuality of SLM exercise were also gathered.
Field watching was carried in order to validate information gained from the husbandman’s via a survey questionnaire. It includes watching of diverse land degradation characters, such as soil erosion and siltation, the incline of agricultural lands, surface runoff and farming activities, involving the types of crops grown, cropping patterns, and on farm soil preservation structures. The sample family leaders were haggard via multi-stage sampling proficiencies. The sampling proficiencies imply three stages. The names of eight villages (two from Engudadar, two from Keswuha, two from Kindomeda, and two from Bazra kebeles) were chosen meaningfully in the first stage. These kebeles were selected based on their agro ecological zones and accessibility. And also, four sample villages, one from each sample kebele, were selected randomly in the second stage. In the third stage, the numbers of all farm families from each chosen sample villages were listed. Finally, 160 male-headed and 40 femal-headed totals of 200 sample farm households of the study were chosen randomly from the four sample villages in proportional to the cover of each agro-climatic zone as shown Table 1. These sample farm households were decided using the following formula .
n=N1+N(e)2(1)
Hence n is the sample size
N is the population size
e is the level of precision (5%).
Based on the above formula, the total sample households were calculated as follows:
n=400/(1+400×0.0025)=200.
Table 1. Distribution of sample farm house holds by district and village level.

Kebele

Village

Total households

Sample farm households

AEZ

Male

Female

Total

Male

Female

Total

Engudadar

Woyinye

18

10

28

1

1

2

Moist-wurch

Kidomeda

Nechilo

122

26

148

59

13

72

Moist-dega

Keswuha

Gandi

80

21

101

40

11

51

Moist-dega

Bazra

Mugieras

143

35

178

60

15

75

Moist-weyna-dega

Total

363

92

455

160

40

200

Level of farmers’ involved in drainage basin management programs is the dependent variable described in this study and the independent variables used in the analysis are given in table below.
Table 2. List of dependent and independent variables.

S.n

Variables

Dependent variable

1

Level of household heads’ involved in a drainage basin management program

Independent variables

1

Off-farm income

2

Family livestock ownership

3

Periodic land redistribution

4

Educational status of the family head

5

Land tenure security of a family

6

Sex of the family head

7

Number of family members involved in farming activities

8

Farm size of the family

9

Oftenness of farming extension visits gained

10

Access to credit services

11

Family heads’ productive safety net beneficiary

12

Slope of the farmland

So, a binary logistic regression model was used to investigate factors affecting farmers’ participation in the watershed management programs in the Northeastern highlands of Ethiopia. As out lined above, this model was used because of the binary nature of the dependent variable (level of participation). Hence, the logistic model is specified as follows .
lnY=lnY/(1−Y)+β0+β1X1+β2X2+β3X3+……+βnXn+ui(2)
Hence,
Y=The predicted probability of the event (farmers’ level of participation in the drainage basin management programs), which is coded with 1= participated; and 0= non-participants
1−Y=The predicted probability of the other decision (non-participants of the watershed management programs)
β0=Constant
βn=Coefficients of explanatory variables
Xn=Predictor variables
Ui=Error term
2.3. Methods of Data Analysis
Both quantitative and qualitative techniques were used to analyze the data of the study. The quantitative data were determined using various statistical tests depend on the level of mensuration of the variables included. According to , Statistical package for social sciences (SPSS-IBM) software, version 21, and Microsoft excel 2010 was used to analyze both inferential and descriptive statistical data (Jan, 2023). We compared and contrasted different classes of sample units with respect to the trusted characteristics by using descriptive statistics. Thus, to see the relationships between explanatory variables and the level of farmers’ participation in drainage basin management programs, we used descriptive statistics such as mean, standard deviation, and percentages. A binary logistic regression model, Pearson correlation, and chi-square also used to understand the correlational statistics between the dependent and independent variables of the study.
Table 3. List of tools used for study.

S.n

Tools

Function

1

(SPSS-IBM) software

To determine both inferential and descriptive statistical data

2

Microsoft excel 2010

To examine both inferential and descriptive statistical data

3

Arc Gis 10.8

To investigate and show Study areas

The level of farmers’ participation in drainage basin management programs was the dependent variable analyzed. Thus, farmers’ participation in a drainage basin management program was measured as a binary dummy variable (1=participated in a drainage basin management program, 0=otherwise). The details of explanatory variables used in the analysis are given in table below.
This part shows the analyses of the binary logistic regression model and defines the personal, physical, and institutional factors influencing farmers’ taking part drainage basin management programs (Table 4).
Table 4. Factors affecting the farmers’ decision to taking part in drainage basin management programs.

Dependent variable

Description

Unit

Y = LFP, Level of Farmers participation

Level of family heads’ taking part in a drainage basin management program

1 if taking part, 0 otherwise

Independent variables

Description

Unit

X1 = OFI, Off-farm income obtained from non-farm activities

Off-farm income

1 if a household is taking part in off-farm activities, 0 otherwise

X2 = LSO, Livestock ownership

Households livestock ownership

Number in TLU

X3 = LRD, Periodic land redistribution

Periodic land redistribution

Yes = 1; No = 2

X4 = ES, Educational status

Educational status of the family head

1 if a family head is literate, 0 otherwise

X5 = LT, Land tenure security

Land tenure protective of a household

Yes = 1; No = 2

X6 = GHH, Gender

Gender of the family head

1 if a household head is male, 0 otherwise

X7 = NALF, Agricultural labor force

Number of family members engaged in agricultural activities

Number

X8 = FS, Farm size

Farm size of the household

Hectare (ha)

X9 = EV, Oftenness of extension visit

Oftenness of farming extension visits received

At least four times in a year = 1; otherwise = 2

X10 = CS, Credit service

Access to credit services

Yes = 1; No= 2

X11 = PSNP, productive safety net program

Family heads’ productive safety net beneficiary

1 if a family head is a PSNP beneficiary, 0 otherwise

X12 = S, Side

Side of the irrigable land

1 if the slope is gentle, 0 otherwise

3. Results
Analyses of factors influencing farmers’ participation in drainage basin management programs
The detailed critical inspection bring out that farmers’ take part in drainage basin management programs is shaped by a complex interplay of personal, physical, institutional, and perceptual factors. Both the econometric and correlation analyses, supported by qualitative insights from focus group discussions (FGDs) and key informant consultations, furnish a comprehensive recognizing of the causal factors act upon take part.
Personal and Household Characteristics
Gender raised as a systematically implication factor crosswise multiple analyses. Both the model outputs and Pearson correlation coefficients indicated an unpleasant and meaningful connection between female-headed families and take part in drainage basin management (Table 3). The chi-square analysis foster corroborated this kinship (X² = 9.052, p < 0.05), with only 23.9% of female-headed families taking part equated to 76.1% of male-headed families. This result aligns with grounds that structural determinants, like limited access to labor, information, and institutional support, disproportionately influence women, despite their vital function in caring available wealth . FGDs also pointed that women usually face heightened surrounding loads, such as longer hours spent fetching scarce water and fuel wood .
Educational status, however, did not significantly affect participation (X² = 2.906, p > 0.05). This may be due to the bottom-up nature of the program, which allows farmers to collectively discuss the long-term importance of drainage startups regardless of formal education levels.
Table 5. The statistical results of the regression analysis.

B

S.E.

Wald

df

Sig.

Exp (B)

95%C.I. forEXP (B)

Lower

Upper

Off-farm income

1.145

0.55

3.155

1

0.064

3.188

0.782

11.375

Livestock holding

0.267

0.133

3.470

1

0.053

1.302

0.975

1.611

Land redistribution

-1.178

0.588

4.000

1

.035*

0.306

0.087

0.981

Land tenure security

−.877

0.510

3.001

1

0.073

0.414

0.144

1.132

Educational status

−.852

0.469

3.223

1

0.059

0.411

0.156

1.067

Gender

−2.588

1.010

5.456

1

.019*

0.065

0.008

0.633

Farming labor force

−555

0.288

3.754

1

.038*

0.545

0.311

0.996

Access to credit service

−.863

0.571

2.137

1

0.129

0.414

0.120

1.331

Farming extension service

−.621

0.161

13.245

1

.000**

0.522

0.370

0.750

Productive safety net program

0.963

0.652

2.074

1

0.150

2.355

0.710

9.921

Farm size

1.742

0.771

5.020

1

.025*

5.705

1.250

26.993

Slope

−1.561

0.468

11.120

1

.001**

0.209

0.081

0.53

Constant

5.611

3.045

3.411

1

0.065

276.503

*P<0.05 **P<0.01

The agricultural labor force showed a negative relationship with participation, suggesting that households with more labor tend to prioritize immediate production activities over conservation measures with delayed returns. This highlights that attitudes and awareness may be more influential than labor availability alone.
Land Tenure, Redistribution, and Farm Characteristics
Land redistribution exhibited a negative and significant effect on participation (Table 4). Frequent reallocations appear to reduce incentives for long-term conservation investments by weakening tenure security, an observation consistent with earlier findings that insecure land tenure discourages land-improving investments . Conversely, land tenure security showed a strong and significant association with participation (X² = 8.691, p < 0.05). Households with documented and secure land rights were more motivated to invest in long-term watershed activities, supporting similar findings by .
Farm size had anticipated positive and significant effect on participation, with larger landholders more willing to invest in watershed activities due to greater expected productivity gains. This outcome concurs with former researches by .
The slope of farmland was negatively associated with participation both in the correlation (Table 5) analysis (r = –0.159, p < 0.05) and the model results. Farmers were less likely to implement conservation measures on steep plots, possibly due to perceived low returns or limited awareness of erosion impacts. This supports findings by .
Table 6. Correlational statistics between continuous independent variables and farmers’ participation.

Variables

(r)

(P) (2-tailed)

Livestock ownership

0.068

0.331

Slope

-0.159ª

0.013

Gender

-0.206b

0.002

Farmland size

0.121

0.079

Family size

0.021

0.761

Off-farm income

-0.028

0.669

Perception

0.6111b

0.000

Government support

0.159ª

0.017

ªCorrelation is significant at the 0.05 level (2-tailed) bCorrelation is significant at the 0.01 level (2-tailed)

Institutional Support and Access to Services
Agricultural extension services displayed an unexpected negative association with participation. Although extension should improve farmers’ knowledge and motivation, its effectiveness may be undermined by inadequate staffing, insufficient logistical support, and the frequent engagement of development agents in non-extension activities . This contrasts with studies reporting positive effects of extension on conservation adoption , underscoring the importance of service quality.
Access to the Productive Safety Net Program (PSNP) and credit services did not significantly influence participation (X² = 3.645 and X² = 1.346, respectively; p > 0.05). Qualitative findings suggested that credit was underutilized due to farmers’ fear of repayment obligations and potential penalties. Similarly, PSNP participation did not appear to shape decisions related to watershed involvement.
Stakeholder support, including assistance from administrative bodies and development partners, also showed no significant association (Table 5) with participation (X² = 0.118, p > 0.05), despite its theoretical importance to confirmable drainage basin management .
Farmers’ Perceptions and Government Support
Perception-related variables showed the strongest influence on participation. Pearson correlation analysis indicated that farmers’ positive perceptions toward watershed programs had a potent and highly meaningful positive correlation with participation (r = 0.612, p < 0.01). Government support also indicated significant convinced association (r = 0.163, p < 0.05). These results highlight that building trust, strengthening communication, and reinforcing perceived benefits are central to improving participation.
Table 7. Descriptive summary of discrete variables.

Variables

Participant (N=164)

Non-participant (N=36)

Chi-square value

Asymp. Sig (2-sided)

Number

%

Number

%

Educational status of the HH head

Literate

39

23.78

14

38.89

2.805

0.077

Illiterate

125

76.22

22

61.11

Gender of the HH head

Male

127

77.44

35

97.22

9.011*

0.002

Female

37

22.56

1

2.78

Access to PSNP

Yes

40

24.39

4

11.11

3.645

0.041

No

124

75.61

32

88.89

Access to credit services

Yes

124

75.61

30

83.33

1.346

0.211

No

40

24.39

6

16.67

Land tenure security

Yes

50

30.49

23

63.89

8.691*

0.002

No

114

69.51

13

36.11

Access to off-farm income

Yes

34

20.73

7

19.44

0.161

0.561

No

130

79.27

29

80.56

Stake holder support

Yes

64

39.02

15

41.67

0.115

0.671

No

100

60.98

21

58.33

Qualitative Insights from FGDs and Key Informant Interviews
FGDs and interviews identified additional contextual factors affecting participation, including poverty, shortage of farmland, drought, inadequate incentives, and unreliable rainfall. More than 90% of FGD participants highlighted land fragmentation, driven by rapid population growth—as a major constraint. Participants also reported governance issues, such as coercion by local administrators and punitive measures for non-participation, including fines and social sanctions. Such practices undermine voluntary participation and may foster negative attitudes toward the program.
Figure 4 revealed that respondents who did not participate in watershed activities (18.1%) cited reasons including deficiency of mindfulness (7.7%), non-existence of additional payment (59%), weak governance (20.5%), and the time-consuming nature of the activities (12.8%). Crucial informants emphasized that livelihood diversification, such as animal fattening, cash crop production, limited scale supplying dry land by water by means of ditches, and water gathering, could help farmers better balance short-term needs with long-term conservation engagement.
Figure 4. Farmers’ reasons for not taking part in drainage basin management programs at current.
Overall, the results demonstrate that take part in drainage basin management programs is affected by a combination of tenure security, household demographic characteristics, farm attributes, perceptions, and the quality of institutional support. Strengthening tenure security, improving extension service quality, enhancing gender-responsive support systems, and building positive perceptions through targeted awareness programs are essential for increasing farmers’ willingness to take part in sustainable drainage basin management.
4. Discussion
This study highlights the multifaceted nature of farmers’ take part in drainage basin management programs, demonstrating that decisions to engage in such initiatives are shaped by interplay of socio-economic factors, land-related attributes, institutional support, and farmers’ perceptions. The findings reinforce that promoting sustainable watershed management requires interventions that address both structural constraints and behavioral determinants.
The negative influence of land redistribution and the positive role of tenure security undermine the critical benefit of stable farm rights in motivating long-term conservation investments. Frequent reallocations reduce farmers’ confidence in securing future benefits from their labor, thereby discouraging participation. This aligns with previous research showing that insecure tenure suppresses incentives to adopt land-improving practices . Strengthening tenure systems, including formal documentation and clear land-use rights, is thus essential for sustaining watershed efforts.
Gender disparities emerged as another significant constraint. Female-headed families were consistently limited right to take part, confirming that gendered inequalities in available source of wealth, working class, information, and institutional support limit women’s engagement in conservation activities. While global evidence shows that closing gender gaps enhances agricultural productivity . The findings suggest that current watershed programs are not sufficiently gender-responsive. Enhancing women’s participation requires tailored support mechanisms, such as labor-saving technologies, targeted training, and inclusive decision-making processes.
Contrary to expectations, neither household labor force nor access to extension services positively influenced participation. The negative association between labor availability and participation suggests that households with more labor prioritize immediate production needs over conservation activities whose financial assistant in time of need accrue in the long term. This highlights the importance of aligning watershed interventions with farmers’ short-term livelihood demands. Even more surprising was the negative relationship with extension contact. Qualitative evidence revealed that the effectiveness of extension services may be compromised by high workloads, limited staffing, and inadequate logistical support for development agents. This finding contrasts with studies demonstrating that well-functioning extension systems positively influence the uptake of conservation technologies , suggesting that improving the quality—not merely the frequency—of extension interactions is crucial.
Farm characteristics also played differentiated roles. Larger farm size increased the likelihood of participation, consistent with former researches , likely because benefits of conservation measures accumulate more noticeably on larger holdings. Conversely, farmers were less likely to implement conservation practices on steep land, possibly due to perceptions of low returns or limited knowledge of erosion risks. This finding confirms earlier reports of farmers’ reluctance to invest in highly erodible fields . Though some studies have found the opposite under different contextual conditions .
Perception-related variables emerged as the strongest positive predictors of participation. Farmers with favorable attitudes toward watershed management and those who perceived greater government support were more willing to participate. This highlights that beyond structural constraints, behavioral and cognitive factors profoundly shape conservation decisions. Thus, awareness creation, participatory planning, and consistent communication about long-term benefits are vital for sustaining engagement.
Several variables traditionally considered important—such as educational status, access to credit, stakeholder support, and PSNP participation—did not show significant associations with participation. The limited effect of credit access may stem from farmers’ fear of repayment risks, while the non-significance of PSNP suggests that food security assistance alone does not ensure engagement in watershed activities. The low influence of stakeholder support may reflect gaps in coordination, communication, or perceived legitimacy of supporting institutions.
Perceptive from FGDs and key informant interviews foster illuminate contextual barriers shaping participation. Poverty, land scarcity due to fragmentation, drought, weak governance, and lack of incentives were frequently identified constraints. Reports of coercive participation practices, including fines and social sanctions, suggest governance challenges that may undermine trust and voluntary engagement. Improving program governance, ensuring transparency, and fostering genuine community participation are therefore essential for strengthening watershed initiatives.
Overall, the discussion indicates that successful watershed management requires a holistic approach that integrates secure land rights, gender-responsive strategies, improved extension quality, and enhanced farmer perceptions. Addressing short-term livelihood priorities through diversification options—such as small-scale irrigation, water harvesting, and livestock fattening—could further support long-term conservation goals. Sustainable watershed management will depend not only on technical interventions but also on social equity, institutional effectiveness, and farmers’ belief in the long-term value of their efforts.
5. Conclusions
This study examined the determinants of farmers’ take part in drainage basin management programs in the Upper Mugie sub-drainage basin, Ethiopia, using econometric investigation, correlation assessment, and qualitative penetrations from focus group discussions and key informant interviews. The determinations exhibit that taking part is formed by a combination of personal, land-related, institutional, and perceptual factors.
From twelve intelligible variables included in the regression model, six significantly influenced farmers’ decisions to participate. Land spread, sex of the family head, farming working class force, extension assistance access, and gradient of agricultural land all exerted significant disconfirming effects on participation. These results highlight the inhibiting roles of tenure insecurity, gender disparities, labor constraints, ineffective extension services, and perceived low returns from conservation on steep land. Conversely, farm size was the only variable showing a good and meaningful effect, showing that families with larger landholdings are much inclined in order to invest at long-term drainage basin conservation activities.
The analysis of discrete variables showed that gender and land tenure security was strongly associated with participation. Female-headed families were significantly limited to take part, reflecting underlying socio-economic constraints that limit their involvement. Likewise, farmers with stronger tenure security were more willing to participate, reinforcing the central role of secure land rights in motivating long-term conservation investments.
Qualitative findings enriched these results by revealing additional contextual constraints, including poverty, land scarcity due to fragmentation, drought, weak governance, absence of payment, and insufficient precipitation. Above 90% of participants described that farmland scarcity is increasing, driven by rapid population growth. Concerns about governance were also prominent, with some farmers reporting coercive participation practices, including monetary penalties and social sanctions for non-compliance. Such practices undermine community trust and threaten the voluntary spirit necessary for sustained program success. Instead of coercion, awareness-raising, inclusive planning, and capacity-building—through training, workshops, and community dialogues—are essential for fostering genuine participation.
Even though, 81.9% of respondents take part in the drainage basin management program, 18.1% did not. Reasons for non-participation included lack of awareness, insufficient incentives, governance challenges, and the time-intensive nature of the activities. Key informants also noted that off-farm engagements, negative attitudes toward the program, limited knowledge, and preference for short-term benefits further discourage participation. These findings underscore the need for livelihood diversification strategies—such as livestock fattening, small-scale irrigation, water harvesting, and cash crop production—to help households balance short-term needs with long-term conservation goals.
Overall, this finding concludes that husbandman involvement in drainage basin management programs remains constrained by a mix of socio-economic, institutional, biophysical, and perceptual barriers. Low levels of awareness, combined with negative influences from insecure land tenure, gender disparities, limited service quality, and governance shortcomings, contribute to reduced engagement. Enhancing participation therefore requires a multi-dimensional approach that strengthens tenure security, improves the quality and responsiveness of extension services, supports gender-inclusive programming, and builds positive perceptions through consistent communication and meaningful community involvement.
Future research should incorporate additional variables—such as farmers’ former go through, reliance in administrator policies, and the effectiveness of local institutions—to deepen the understanding of participation dynamics and strengthen predictive capacity. Such insights will be essential for designing more targeted, equitable, and sustainable watershed management interventions.
Abbreviations

GDP

Gross Domestic Productivity

SWC

Soil and Water Preservation

AMSL

Above Mean Sea Level

FGDS

Focus Group Discussions

SLM

Sustainable Land Management

SPSS

Statistical Package for Social Sciences

GIS

Geographical Information System

LFP

Level of Farmers Participation

OFI

Off-farm Income

LSO

Livestock Ownership

LRD

Land Redistribution

ES

Educational Status

LT

Land Tenure Security

GHH

Gender of the Household Head

NALF

Number of Agricultural Labor Force

FS

Farm Size

EV

Extension Visit

CS

Credit Service

PSNP

Productive Safety Net Program

Author Contributions
Agmasie Belay: Conceptualization, Data curation, Methodology, Resources
Tibebe Tigabu: Investigation, Supervision, Visualization, Writing – review & editing
Conflicts of Interest
The authors declare no conflicts of interest.
References
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    Belay, A., Tigabu, T., Assefa, T. (2026). Factors Affecting Farmers’ Participation in Watershed Management Programs in Northern Ethiopia: A Case Study in the Upper Mugie Sub-watershed. International Journal of Environmental Protection and Policy, 14(3), 71-83. https://doi.org/10.11648/j.ijepp.20261403.12

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    Belay, A.; Tigabu, T.; Assefa, T. Factors Affecting Farmers’ Participation in Watershed Management Programs in Northern Ethiopia: A Case Study in the Upper Mugie Sub-watershed. Int. J. Environ. Prot. Policy 2026, 14(3), 71-83. doi: 10.11648/j.ijepp.20261403.12

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    AMA Style

    Belay A, Tigabu T, Assefa T. Factors Affecting Farmers’ Participation in Watershed Management Programs in Northern Ethiopia: A Case Study in the Upper Mugie Sub-watershed. Int J Environ Prot Policy. 2026;14(3):71-83. doi: 10.11648/j.ijepp.20261403.12

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  • @article{10.11648/j.ijepp.20261403.12,
      author = {Agmasie Belay and Tibebe Tigabu and Tewodros Assefa},
      title = {Factors Affecting Farmers’ Participation in Watershed Management Programs in Northern Ethiopia: A Case Study in the Upper Mugie Sub-watershed},
      journal = {International Journal of Environmental Protection and Policy},
      volume = {14},
      number = {3},
      pages = {71-83},
      doi = {10.11648/j.ijepp.20261403.12},
      url = {https://doi.org/10.11648/j.ijepp.20261403.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijepp.20261403.12},
      abstract = {The purpose of this study was to evaluate the factors influencing farmers’ participation in watershed management in the Mugie Sub-watershed, located in the northeastern highlands of Ethiopia. A combination of purposive and random sampling techniques was used to select 200 households from four villages. Data was collected using a structured survey questionnaire, focus group discussions, and key informant interviews. The data were analyzed using a range of statistical techniques, including descriptive statistics, Pearson correlation, and regression analysis. The results revealed that farmers’ perception was strongly correlated (r = 0.612, p < 0.01) with their decision to participate in watershed management programs, followed by stakeholders’ support (r = 0.163, p < 0.05). In contrast, the slope of the farmland and the gender of the household head showed significant negative associations. Binary logistic regression analysis further indicated that six independent variables were important in explaining farmers’ decisions to participate in watershed management programs. These variables included land redistribution, gender, family labor force, educational opportunity, farm size, and land slope. Land redistribution, gender, family labor force, educational opportunity, and land slope had negative effects, whereas farm size had a positive effect. Further analysis also demonstrated the role of individual variables in explaining variation in farmers’ decisions to participate in the program. Among these, two variables were found to be statistically significant: the gender of the household head and land tenure security. Accordingly, the chi-square value for gender (X2 = 9.052) was statistically significant at the 95% confidence level. Similarly, the chi-square value for land tenure security (X2 = 8.691) was also statistically significant at the 95% confidence level. The findings of the study suggest the need to raise farmers’ awareness of the long-term benefits of watershed management programs and to design strategies that help diversify their livelihoods.},
     year = {2026}
    }
    

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  • TY  - JOUR
    T1  - Factors Affecting Farmers’ Participation in Watershed Management Programs in Northern Ethiopia: A Case Study in the Upper Mugie Sub-watershed
    AU  - Agmasie Belay
    AU  - Tibebe Tigabu
    AU  - Tewodros Assefa
    Y1  - 2026/06/29
    PY  - 2026
    N1  - https://doi.org/10.11648/j.ijepp.20261403.12
    DO  - 10.11648/j.ijepp.20261403.12
    T2  - International Journal of Environmental Protection and Policy
    JF  - International Journal of Environmental Protection and Policy
    JO  - International Journal of Environmental Protection and Policy
    SP  - 71
    EP  - 83
    PB  - Science Publishing Group
    SN  - 2330-7536
    UR  - https://doi.org/10.11648/j.ijepp.20261403.12
    AB  - The purpose of this study was to evaluate the factors influencing farmers’ participation in watershed management in the Mugie Sub-watershed, located in the northeastern highlands of Ethiopia. A combination of purposive and random sampling techniques was used to select 200 households from four villages. Data was collected using a structured survey questionnaire, focus group discussions, and key informant interviews. The data were analyzed using a range of statistical techniques, including descriptive statistics, Pearson correlation, and regression analysis. The results revealed that farmers’ perception was strongly correlated (r = 0.612, p < 0.01) with their decision to participate in watershed management programs, followed by stakeholders’ support (r = 0.163, p < 0.05). In contrast, the slope of the farmland and the gender of the household head showed significant negative associations. Binary logistic regression analysis further indicated that six independent variables were important in explaining farmers’ decisions to participate in watershed management programs. These variables included land redistribution, gender, family labor force, educational opportunity, farm size, and land slope. Land redistribution, gender, family labor force, educational opportunity, and land slope had negative effects, whereas farm size had a positive effect. Further analysis also demonstrated the role of individual variables in explaining variation in farmers’ decisions to participate in the program. Among these, two variables were found to be statistically significant: the gender of the household head and land tenure security. Accordingly, the chi-square value for gender (X2 = 9.052) was statistically significant at the 95% confidence level. Similarly, the chi-square value for land tenure security (X2 = 8.691) was also statistically significant at the 95% confidence level. The findings of the study suggest the need to raise farmers’ awareness of the long-term benefits of watershed management programs and to design strategies that help diversify their livelihoods.
    VL  - 14
    IS  - 3
    ER  - 

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