Agriculture is the backbone of Nepal's economy, with the Terai region, characterized by fertile alluvial soil, hosting the majority of irrigation systems. However, ageing infrastructure, inadequate maintenance, and poor project prioritization have severely impacted agricultural productivity. This study addresses these challenges by employing a multi-criteria decision-making (MCDM) approach to prioritize irrigation projects based on critical performance indicators such as water conveyance efficiency, application efficiency, and cropping intensity. Field data, including soil moisture, infiltration rates, and evapotranspiration, along with survey data, were utilized to assess five irrigation projects. Results identified the Kiran Nala Lift Irrigation Project as the highest priority for maintenance, while the Rajapur Irrigation Project ranked the lowest. This pioneering application of MCDM in Nepal's irrigation sector provides a robust framework for project prioritization, offering critical insights for improving agricultural productivity through targeted interventions. Practical Applications: This research applies the MCDM approach to assess irrigation projects based on nine key criteria, including efficiency metrics and environmental factors. By systematically addressing the infrastructure and management challenges, this study provides a scientific basis for optimizing irrigation project operations. The findings serve as an actionable tool for policymakers to enhance agricultural output by prioritizing the maintenance of critical irrigation systems.

  • First multi-criteria decision-making application for irrigation in Nepal, enhancing project prioritization in the Terai region.

  • Field-based data on nine irrigation performance criteria, ensuring accurate evaluation.

  • Practical framework for improving agricultural productivity through project ranking.

  • Focus on southern Nepal, addressing inefficiencies in critical agricultural zones.

  • Actionable insights for policymakers, guiding infrastructure decisions.

Agriculture is the primary commodity of most developing countries, providing livelihoods and employment opportunities for people. In Nepal, about 66% of the population depends on agriculture, yet the sector contributes only 20% to the gross domestic production while employing 65% of the labor force (MoF 2021). Despite having 4.12 million hectares (ha) of cultivable land (MoALD 2022), only 39% of this area receives year-round irrigation (DoWRI 2019a), leading to agricultural instability and increasing reliance on imports. In 2022, agricultural imports surged by 18% from the previous year, overshadowing exports by a factor of seven (MoALD 2022). Several factors compound these challenges: high population density, limited cultivated area, traditional farming practices, rising pesticide costs, fertilizer shortages, and the impact of climate change all contribute to low agricultural productivity (Kumar et al. 2022; Shanmugavel et al. 2023). Furthermore, low irrigation efficiency, siltation in canals and fields, unmanaged irrigation practices, low investment in the irrigation sector, and lack of regular operation and management are the key challenges for the development of reliable irrigation facilities (Pradhan & Belbase 2018). Rapid urbanization has exacerbated the situation by encroaching on agricultural land and increasing food demand. The growing disparity between agricultural supply and demand jeopardizes both the national economy and food security (Kang et al. 2023). Addressing these issues requires expanding year-round stable irrigation and implementing robust systems supported by proper operation and regular maintenance.

The Terai region is the southernmost part of Nepal, consisting of fertile alluvial plains that support the majority of the country's agricultural activities. The region is characterized by a subtropical climate with high seasonal rainfall, predominantly during the monsoon season. The flat topography, combined with the presence of three major Himalayan river systems (Koshi, Gandaki, and Karnali), makes it a crucial agricultural hub. However, irrigation remains a major challenge due to sedimentation, inefficient water distribution, and inadequate infrastructure. Only a small fraction of it is used for irrigation in the Terai region. Among the available agricultural land in Terai, only 18% receives year-round irrigation (DoWRI 2019a). The complex terrain and substantial investment costs make it difficult to harness water from these major river systems leading to the reliance on medium- and small-sized rivers (Bista et al. 2021), groundwater, and erratic rainfall. Although 25 irrigation systems with a command area exceeding 25 ha are operational in the Terai, covering a net command area of 303,799 ha, the canal network is deteriorating, and hydraulic structures have exceeded their design life. Silt deposition in canals further disrupts water distribution and reduces operational efficiency. Because of gravity-fed irrigation systems, water is typically diverted into canals using overflow weirs or barrages, which regulate the flow from rivers. While these structures ensure a continuous water supply, they also introduce significant amounts of sediment into the canal network. Excessive sedimentation leads to canal clogging, reduced carrying capacity, and decreased irrigation efficiency. Regular sediment management through desilting and controlled flushing is essential to maintain canal performance. Sedimentation affects canal carrying capacity by reducing the cross-sectional area of flow. A heavily silted canal may operate at only 50% of its design discharge, limiting the area that can be irrigated. Desilting programs can restore flow capacity, potentially increasing the command area by up to 20% without additional infrastructure investment. This suggests that projects like Rajapur and Narayani, which suffer from high sedimentation, could benefit significantly from targeted desilting initiatives.

With limited financial resources, constructing new structures for efficient distribution, silt removal, and complete rehabilitation is prohibitively expensive. Consequently, selecting the most effective irrigation system for maximizing agricultural productivity has become increasingly challenging under these constraints. While constructing a new irrigation infrastructure is costly, regular maintenance and modernization are necessary for sustaining irrigation efficiency. Many international donor agencies prioritize investment in large-scale projects where the cost-benefit ratio is high. However, targeted interventions, such as selective infrastructure rehabilitation and improved sediment management, can significantly enhance irrigation efficiency without requiring prohibitively high capital investments.

The government of Nepal has an ambitious goal to increase agricultural production by 80% by the end of 2030 (DoWRI 2019b). To achieve this objective, the number of irrigation projects has to be increased, making the effective operation and maintenance (O&M) of the existing systems essential. Balancing new investments with O&M costs is crucial to ensure the sustainable development of irrigation infrastructure (Mwendera & Chilonda 2013). These O&M costs can be achieved either through government subsidies or water taxes from the farmers. However, with both mechanisms not functioning effectively, the budget for maintenance remains limited. On the other hand, poor maintenance reduces the active life of a project. Given the need to strengthen and expand the existing agricultural land, project prioritization becomes a critical element in investment planning and the sustainable development of irrigation facilities.

The overall performance of the project depends on various performance indicators like efficiencies, moisture content, soil type, and infiltration rate, among others. A project achieves higher performance and greater agricultural production if individual criteria are met effectively, justifying a higher priority for that project. The selection of these criteria is based on the evaluation metrics for investment and O&M, which are crucial factors in the decision-making process. In this context, MCDM techniques provide a powerful framework for evaluating various factors in decision-making (Köhler et al. 2019). These techniques enhance transparency, auditability, and analytic rigor in decision-making (Dunning et al. 2000). While several qualitative and quantitative methods can be employed to prioritize projects, MCDM techniques are particularly effective when reliable information is available. This approach evaluates multiple alternatives based on different criteria to select the best option. Consequently, MCDM techniques have been extensively used to develop strategies for agricultural water management (Radmehr et al. 2022), prioritize and select agricultural irrigation systems (Veisi et al. 2023), prioritize adaptation measures for agriculture (Acharjee et al. 2020), identify erosion-prone watersheds (Sarkar et al. 2022), manage sustainable energy (Arayeh 2015), delineate potential groundwater recharge areas (Lamichhane & Shakya 2019), and map flood hazards (Mudashiru et al. 2022).

These studies focus on prioritizing projects based on different alternatives and selecting the best option for planning and development. However, the application of MCDM techniques for prioritizing irrigation projects based on O&M remains limited. The objectives of this study are to (i) collect data on irrigation criteria of five projects through field survey, testing, measurement, and stakeholder interactions, (ii) conduct a questionnaire survey with expert consultations, and (iii) prioritize the best irrigation project based on criteria weights using the analytical hierarchy process (AHP). This method involves pairwise comparison of the alternatives for each criterion, followed by aggregation to compute the overall score (Saaty & Vargas 2022). This study addresses the dearth of MCDM-based project prioritization in the context of irrigation O&M, providing insights for more effective investment planning and irrigation development in Nepal.

Study area

We selected five irrigation projects for this study: (a) Rajapur Irrigation Project, (RIP) (b) Kiran Nala Lift Irrigation System (KNLIS), (c) Narayani Irrigation System (NIS), (d) Manushmara Irrigation System-Phase 1 (MISP1), and (e) Kamala Hardinath Irrigation System (KHIS), as shown in Figure 1. These irrigation projects are located south of the Siwalik region and are highly dependent on monsoon rainfall and groundwater discharge.
Figure 1

Location of the study area along with a stream network and a command area.

Figure 1

Location of the study area along with a stream network and a command area.

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RIP is a gravity-flow irrigation system located in Bardiya district, Nepal. It covers a command area of 14,880 ha and is situated between the Karnali River to the west and the Giruea River to the east, as shown in Figure 1(a). RIP is one of the largest farmer-managed irrigation systems in the region, relying primarily on the flow from the Giruea River flow. Most of the cross and head regulators of the project were found to be ungated, affecting its operational efficiency.

KNLIS with a command area of 250 ha is located in Banke district, as shown in Figure 1(b). Kiran Nala River is the primary source of irrigation for KNLIS.

NIS has the command area of 37, 400 ha, located in Parsa district, as shown in Figure 1(c). Narayani River is the primary source of irrigation for NIP, with a barrage constructed to divert water into the system. The eastern canal, 92 km long with a capacity of 850 m3/s, exhibits signs of deterioration, resulting in only approximately 30% of the command area receiving consistent year-round irrigation. Notably, heavy silt deposition near the head regulator and the absence of effective silt exclusion measures along the main canal exacerbated the issue. Although a silt ejector was installed at the head race of the main canal, its functionality was compromised, contributing to inadequate silt removal.

MISP1, located in Sarlahi district, has a command area of 2, 214 ha, Figure 1(d). The system depends on the Manushmara River, a spring water source, for irrigation. The canal network and hydraulic structures have deteriorated and passed the design life. Large amounts of silt were also observed along the bed and side of the canal, further impeding water flow.

KHIS is one of the largest public irrigation systems, with a command area of 25,000 ha in the Siraha district, Figure 1(e). It was primarily designed to provide supplemental irrigation for monsoon paddy. The Kamala River, a perennial river, is the primary source of irrigation for KHIS. Like the other systems, the canal and hydraulic structures deteriorate over time, with significant silt deposition observed along the canal bed and sides.

Methodology

The performance of an irrigation project depends on several criteria, including conveyance efficiency, water application efficiency, soil type, infiltration rate, soil moisture, evapotranspiration, crop intensity, and command area. To comprehensively assess these factors, we conducted field measurements and tests as the primary step. Subsequently, a questionnaire survey was undertaken, engaging diverse groups of stakeholders, including farmers, officials, engineers, consultants, and other relevant experts. Their insights and expertise were collected to assign appropriate scores, on a scale of 1–9, to each parameter, thereby capturing the ground truth. The average score for each parameter was then utilized for further analysis (Table 3).

We employed the AHP method as the analytical framework for project prioritization. This involves developing pairwise comparison matrices and normalized matrices to facilitate AHP computation. The AHP method was chosen for its ability to handle complex decision-making processes involving multiple criteria. Project prioritization was then executed based on the estimated weighted factors assigned to each parameter. This approach allowed us to synthesize various criteria into a single, comprehensive evaluation of each irrigation project's priority for O&M. The overall study framework is shown in Figure 2, highlighting the key steps from data collection through to the final project prioritization.
Figure 2

Methodological framework for project prioritization (AHP: analytical hierarchical process, MCDM: multi-criteria decision-making and CR: consistency ratio).

Figure 2

Methodological framework for project prioritization (AHP: analytical hierarchical process, MCDM: multi-criteria decision-making and CR: consistency ratio).

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Field measurement and data collection

Command area

The command area data for the projects were collected from the Water Resource Research and Development Centre, Nepal.

Soil type

Soil type influences the amount of water that can be retained in soil per unit depth. Sandy soil can store a significantly smaller amount of water for a short period compared to clay soil, demanding more frequent water application. The soil characteristics of the irrigation projects were assessed through field observation and surface exploration. Sieve analysis and soil gradation tests were conducted on the soil type in each project area.

Soil moisture (initial and final)

Moisture content was measured at various locations in the grid (10 × 4 m) using a soil moisture sensor with a reading head and a 30 cm probe rod, as shown in Figure 3. Initial and final moisture content measurements were taken before and after the irrigation event, respectively.
Figure 3

Layout for the soil moisture measurement in a plot (left) and its measurement using a soil moisture sensor before water application.

Figure 3

Layout for the soil moisture measurement in a plot (left) and its measurement using a soil moisture sensor before water application.

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Infiltration rate

Infiltration rate is a key process through which water is lost from the soil profile. It is influenced by soil texture and structure. The infiltration rate is typically higher during dry conditions and decreases gradually as the soil becomes saturated. The continuous application of water eventually leads to surface runoff and a constant infiltration rate. Various types of infiltrometers have been used to measure soil infiltration. Among them, we used a double-ring infiltrometer (a 30 cm inner and a 60 cm outer ring, each with 27 cm height), which provides better performance. The rings were placed concentrically and driven uniformly 15 cm into the ground, as shown in Figure 4. The infiltration rate was measured following the guidelines provided by the Food and Agriculture Organization's guideline (FAO 2004).
Figure 4

Layout for the infiltration test (left) and its measurement using a double-ring infiltrometer.

Figure 4

Layout for the infiltration test (left) and its measurement using a double-ring infiltrometer.

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Evapotranspiration

Evapotranspiration is the loss of water due to evaporation from the soil surface and transpiration through the crop. It is influenced by weather conditions (solar radiation, air temperature, humidity, and wind speed), crop factors (crop type, ground coverage, and root density), soil characteristics (moisture and salinity), and management practices (mulching, shading, and fertilizer application). Accurate estimation of evapotranspiration is essential for planning, designing, and operating irrigation systems. The Penman–Monteith method (Monteith 1965) was used to estimate the potential evapotranspiration. It operates on solar radiation, air temperature, relative humidity, and wind speed. These data were collected from the Department of Hydrology and Meteorology, Nepal.

Cropping intensity

Cropping intensity refers to the number of planting cycles within a year (Pan et al. 2021). It is the primary factor affecting crop production and agricultural intensification (Biradar & Xiao 2011). Cropping intensity is calculated as the ratio of the gross command area to the net sown area. An increase in cropping intensity boosts crop production and enhances the farmer's economic returns.

Water application efficiency

Water application efficiency measures how effectively the irrigation system delivers water from the conveyance system to the crop. It was calculated using the following equations:
(1)
(2)
where is the water application efficiency, and are the volumes (m3) of the irrigation water stored in the root zone and delivered to the field, respectively. and are the final and initial moisture contents, Z is the root zone depth (cm), and A is the area of the plot.
The volume of water applied to the plot was measured using the V-notch method, as shown in Figure 5. The method is simple and highly sensitive to the depth of flow, necessitating careful calibration of the V-notch before file measurements. The root zone depth of plants was estimated following FAO guidelines (FAO 2004).
Figure 5

Field calibration of the V-notch.

Figure 5

Field calibration of the V-notch.

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Conveyance efficiency

Conveyance efficiency is the amount of water delivered from the source to the field and depends on the characteristics of the conveyance structure (Haymale et al. 2020). Conveyance efficiency is a significant component of the irrigation system that affects water availability for crops and the efficiency of water application (Hashemy Shahdany et al. 2019; Zhen et al. 2019). Poor management often leads to water wastage. A reliable delivery of water becomes challenging during the dry season, particularly in rain-fed regions (Zhu et al. 2019; Bista et al. 2024). Water is lost along the canal through evaporation, seepage, and overtopping with the magnitude, which largely depend on canal length. Flow measurements at different sections of the main and branch canals were conducted using a current meter (vertical axis type, 5-inch bucket diameter, 2% accuracy). A schematic of the irrigation scheme with discharge measurement locations is shown in Figure 6. Conveyance efficiency for the main and branch canals was estimated using the following equation:
(3)
where is the conveyance efficiency, and are the flow rates (m3/s) at the source (head) and the field (tail) end of the canal, respectively.
Figure 6

Layout of the irrigation scheme on the left shows flow measurement marked in red at various canal sections. The photograph on the right demonstrates flow measurement in the main canal using a current meter.

Figure 6

Layout of the irrigation scheme on the left shows flow measurement marked in red at various canal sections. The photograph on the right demonstrates flow measurement in the main canal using a current meter.

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Formulation of questionnaires

Seventeen questions (Supplementary S1) were prepared and distributed among the experts, including engineers, project managers, farmers, and other stakeholders, to assign scores to the field criteria. The comparison judgment scale proposed by Saaty (1980) was used for the assignment of scores to the criteria. The scale ranges from 1 to 9, where 1 indicates equally important and 9 indicates the most important. The reciprocal value (1/1–1/9) indicates the least importance. The questionnaires and criteria are available in the Supplementary Section (S1).

Formulation of MCDM

MCDM is used to prioritize alternatives based on multiple criteria, making it particularly useful in decision-making where various parameters influence the outcome (Triantaphyllou 2000; Ozsahin et al. 2021). Since these parameters may have different units, normalization is applied to make values comparable. We employed the linear maximum and sum-based normalization methods, as suggested by Vafaei et al. (2016), ensuring that the sum of each column equals one (Saaty 1980). Logarithmic normalization was avoided due to its potential to produce zero or infinite values, making it unsuitable for the AHP method.

AHP, a widely used MCDM technique, structures decision-making into a hierarchy where weighted factors determine prioritization (Saaty 1980). The process involves (i) forming a pairwise comparison matrix based on expert scores (ranging from 1 to 9), (ii) normalizing data into unit-less values, (iii) assessing consistency to minimize bias, and (iv) ranking alternatives based on their relative importance (Saaty 1980; Saifullah 2019). The assigned weights significantly impact the final prioritization outcome.

To check the consistency of the pairwise comparison matrix, we calculated the consistency ratio (CR) as a ratio of the consistency index (CI, Equation (4)) to the average random index (RI).
(4)
where is the maximum eigenvalue of the matrix shown in Table 5 and n is the number of the criteria.
The ideal value of CI is zero, indicating that the pairwise comparison matrix is consistent. The CR is calculated using the following equation:
(5)

The value of RI depends on the number of criteria selected for the study. For this study, we used nine criteria, corresponding to the RI value of 1.45 suggested by Saaty (1980). The value of CR less than or equal to 10% is considered as rational.

In this study, weighted factors are assigned to the criteria based on expert preference to account for the specific context of the problem. The weight of each criterion was calculated using the following equation. Detailed calculations can be found in Table 5.
(6)
where is the weighted factor for criteria i; is the weighted scored on criteria i, and n is the number of the criteria.
The normalized scores of field criteria were multiplied with the respective weighted factors calculated from the AHP method and summed to gate the prioritization index (Equation (7)) for each project. The project with the higher index was ranked first, indicating the higher priority for O&M.
(7)
where PI is the prioritization index and is the normalized score for the ith criteria.

Measurement of field criteria

Nine criteria were chosen based on previous studies. These parameters were measured in the field for different irrigation projects. The difference between each criterion and irrigation performance and productivity is presented in Table 1. NIS is the largest irrigation project, characterized by dominant clay soil with the lowest infiltration rate (3.66 mm/h) and conveyance efficiency (41%), among the selected projects. It has a cropping intensity of 105% and a water application efficiency of 48%. KNLIS is the smallest project but demonstrates the highest conveyance efficiency (67.26%) and cropping intensity (147%). Clay loam soil with an infiltration rate of 5.57 mm/h is dominant in this project. RIP is dominated by sandy soil with a high infiltration rate (61.50 mm/h). Conveyance efficiency directly impacts the volume of water available for irrigation. For each additional percentage point increase in conveyance efficiency, there is a proportional increase in the volume of water delivered to fields, which can lead to a significant rise in crop yields. For instance, an increase in water availability from 40 to 60% efficiency could result in a 30–50% improvement in crop productivity, depending on soil and climate conditions. Also, sedimentation affects the canal carrying capacity by reducing the cross-sectional area of flow. A heavily silted canal may operate at only 50% of its design discharge, limiting the area that can be irrigated. Desilting programs can restore flow capacity, potentially increasing the command area by up to 20% without additional infrastructure investment. This suggests that projects like Rajapur and Narayani, which suffer from high sedimentation, could benefit significantly from the targeted desilting initiatives. The summary of the field measurement is shown in Table 2.

Table 1

Importance of field criteria

S.N.CriteriaImportance to system analysis
Command area (CA) Large CA means large area, high beneficiaries, and more productivity 
Soil type Clay and clay loam soil are more beneficial than sandy soil 
Initial soil moisture (ISM) Means moisture retains the capacity of soil before irrigation; the high value of ISM provides better performance of the system. 
Final soil moisture (FSM) Difference in moisture content between FSM and ISM used for productivity; so, high value means better performance 
Infiltration rate Means the rate of water passing from the surface to the subsurface. High value produces less application efficiency 
Evapotranspiration Means the rate of moisture escape from the field due to various meteorological conditions. High value means less performance of the project. 
Cropping intensity High intensity means high productivity with the same supply water 
Water application efficiency High value indicates maximum utilization of moisture, so that increases the productivity 
Conveyance efficiency High rate shows that water has to be saved for the other expanded area for productivity 
S.N.CriteriaImportance to system analysis
Command area (CA) Large CA means large area, high beneficiaries, and more productivity 
Soil type Clay and clay loam soil are more beneficial than sandy soil 
Initial soil moisture (ISM) Means moisture retains the capacity of soil before irrigation; the high value of ISM provides better performance of the system. 
Final soil moisture (FSM) Difference in moisture content between FSM and ISM used for productivity; so, high value means better performance 
Infiltration rate Means the rate of water passing from the surface to the subsurface. High value produces less application efficiency 
Evapotranspiration Means the rate of moisture escape from the field due to various meteorological conditions. High value means less performance of the project. 
Cropping intensity High intensity means high productivity with the same supply water 
Water application efficiency High value indicates maximum utilization of moisture, so that increases the productivity 
Conveyance efficiency High rate shows that water has to be saved for the other expanded area for productivity 
Table 2

Criteria measured in the field

S. No.ProjectsCommand area (ha)Soil typeInitial soil moisture (%)Final soil moisture (%)Average Infiltration rate (mm/h)Evapotranspiration (mm/day)Cropping intensity (%)Water Application efficiency (%)Conveyance efficiency (%)
RIP 14,880 Sandy soil 10.97 19.13 61.50 3.13 105.00 54.00 45.00 
KNLIS 250 Claye loam 15.70 22.90 5.57 3.08 147.00 48.31 67.26 
NIS 37,400 Clay 7.50 15.90 3.66 3.31 105.00 48.00 41.00 
MISP1 2,214 Clay and loamy clay 18.07 22.83 6.24 3.36 145.00 47.00 51.00 
KHIS 25,000 Sandy and sandy loamy 10.42 18.65 24.00 3.17 105.00 52.00 55.00 
S. No.ProjectsCommand area (ha)Soil typeInitial soil moisture (%)Final soil moisture (%)Average Infiltration rate (mm/h)Evapotranspiration (mm/day)Cropping intensity (%)Water Application efficiency (%)Conveyance efficiency (%)
RIP 14,880 Sandy soil 10.97 19.13 61.50 3.13 105.00 54.00 45.00 
KNLIS 250 Claye loam 15.70 22.90 5.57 3.08 147.00 48.31 67.26 
NIS 37,400 Clay 7.50 15.90 3.66 3.31 105.00 48.00 41.00 
MISP1 2,214 Clay and loamy clay 18.07 22.83 6.24 3.36 145.00 47.00 51.00 
KHIS 25,000 Sandy and sandy loamy 10.42 18.65 24.00 3.17 105.00 52.00 55.00 

Questionnaire survey

The average score by experts on nine field criteria during the questionnaire survey is presented in Table 3. It indicates the importance of criteria with respect to others. We conducted a questionnaire survey involving twenty participants (officials, engineers, consultants, farmers, and others) to acquire diversified information for generating the pairwise comparison matrix.

Table 3

Average score on each criterion assigned by experts in the questionnaire survey

S. NoCriteria123456789
Conveyance efficiency 
Application efficiency  
Soil type   
Average infiltration rate    
Final soil moisture     
Initial soil moisture      
Crop intensity       
Evapotranspiration        
Command area         
S. NoCriteria123456789
Conveyance efficiency 
Application efficiency  
Soil type   
Average infiltration rate    
Final soil moisture     
Initial soil moisture      
Crop intensity       
Evapotranspiration        
Command area         

Pairwise comparison matrix and normalization matrix

The pairwise comparison matrix was developed (Table 4), and reversal was done with the respective criteria for the application of the AHP method. For instance, conveyance efficiency is considered nine times more important than the command area. We then developed a normalization matrix to rank the alternatives, as shown in Table 5. We used CR to assess the suitability of normalization techniques and compared it with the table value using a linear normalization technique. The analysis resulted in a CI of 0.14 based on the comparison matrix and the normalization matrix. The CR is calculated as 0.09 (<0.10, within the acceptable limit). These results indicate that the pairwise compression matrix and normalization matrix provided consistent output among the criteria, and the generated weights of each criterion provided realistic information.

Table 4

Pairwise comparison matrix

S. NoCriteria (Wsi)123456789
Conveyance efficiency 
Application efficiency 0.5 
Soil type 0.33 0.5 
Average infiltration rate 0.25 0.33 0.5 
Final soil Moisture 0.17 0.25 0.33 0.5 
Initial soil moisture 0.17 0.2 0.25 0.33 0.5 
Crop intensity 0.14 0.17 0.2 0.2 0.33 0.5 
Evapotranspiration 0.13 0.14 0.14 0.17 0.2 0.2 0.5 
Command area 0.11 0.11 0.13 0.14 0.14 0.14 0.2 0.5 
 ∑Wsi 2.8 4.7 7.55 11.34 16.18 21.84 29.7 41.5 55 
S. NoCriteria (Wsi)123456789
Conveyance efficiency 
Application efficiency 0.5 
Soil type 0.33 0.5 
Average infiltration rate 0.25 0.33 0.5 
Final soil Moisture 0.17 0.25 0.33 0.5 
Initial soil moisture 0.17 0.2 0.25 0.33 0.5 
Crop intensity 0.14 0.17 0.2 0.2 0.33 0.5 
Evapotranspiration 0.13 0.14 0.14 0.17 0.2 0.2 0.5 
Command area 0.11 0.11 0.13 0.14 0.14 0.14 0.2 0.5 
 ∑Wsi 2.8 4.7 7.55 11.34 16.18 21.84 29.7 41.5 55 
Table 5

Normalization matrix and weighted factor of criteria

S. No.Criteria123456789SumAverage weighted
Conveyance efficiency 0.36 0.43 0.4 0.35 0.31 0.27 0.24 0.19 0.16 2.71 0.30 
Application efficiency 0.18 0.21 0.26 0.26 0.25 0.23 0.2 0.17 0.16 1.93 0.21 
Soil type 0.12 0.11 0.13 0.18 0.19 0.18 0.17 0.17 0.15 1.39 0.15 
Average infiltration rate 0.09 0.07 0.07 0.09 0.12 0.14 0.17 0.14 0.13 1.02 0.11 
Final soil moisture 0.06 0.05 0.04 0.04 0.06 0.09 0.1 0.12 0.13 0.70 0.08 
Initial soil moisture 0.06 0.04 0.03 0.03 0.03 0.05 0.07 0.12 0.13 0.56 0.06 
Crop intensity 0.05 0.04 0.03 0.02 0.02 0.02 0.03 0.05 0.09 0.35 0.04 
Evapotranspiration 0.04 0.03 0.02 0.01 0.01 0.01 0.02 0.02 0.04 0.21 0.02 
Command area 0.04 0.02 0.02 0.01 0.01 0.01 0.01 0.01 0.02 0.14 0.02 
n = 9   
S. No.Criteria123456789SumAverage weighted
Conveyance efficiency 0.36 0.43 0.4 0.35 0.31 0.27 0.24 0.19 0.16 2.71 0.30 
Application efficiency 0.18 0.21 0.26 0.26 0.25 0.23 0.2 0.17 0.16 1.93 0.21 
Soil type 0.12 0.11 0.13 0.18 0.19 0.18 0.17 0.17 0.15 1.39 0.15 
Average infiltration rate 0.09 0.07 0.07 0.09 0.12 0.14 0.17 0.14 0.13 1.02 0.11 
Final soil moisture 0.06 0.05 0.04 0.04 0.06 0.09 0.1 0.12 0.13 0.70 0.08 
Initial soil moisture 0.06 0.04 0.03 0.03 0.03 0.05 0.07 0.12 0.13 0.56 0.06 
Crop intensity 0.05 0.04 0.03 0.02 0.02 0.02 0.03 0.05 0.09 0.35 0.04 
Evapotranspiration 0.04 0.03 0.02 0.01 0.01 0.01 0.02 0.02 0.04 0.21 0.02 
Command area 0.04 0.02 0.02 0.01 0.01 0.01 0.01 0.01 0.02 0.14 0.02 
n = 9   

Note:.

Example: which is calculated as 0.30.

S. No.CriteriaAverage weightedRankConsistency measure
Conveyance efficiency 0.3 9.98 
Application efficiency 0.21 10.12 
Soil type 0.15 10.08 
Average infiltration rate 0.11 9.94 
Final soil moisture 0.08 9.69 
Initial soil moisture 0.06 9.30 
Crop intensity 0.04 9.19 
Evapotranspiration 0.02 9.18 
Command area 0.02 9.19 
n = 9    CI = 0.14 
S. No.CriteriaAverage weightedRankConsistency measure
Conveyance efficiency 0.3 9.98 
Application efficiency 0.21 10.12 
Soil type 0.15 10.08 
Average infiltration rate 0.11 9.94 
Final soil moisture 0.08 9.69 
Initial soil moisture 0.06 9.30 
Crop intensity 0.04 9.19 
Evapotranspiration 0.02 9.18 
Command area 0.02 9.19 
n = 9    CI = 0.14 

Note: and where, RI is 1.45 for nine criteria (Saaty 1980). Therefore, CR is computed to be 0.09.

Consistency measure for a criteria = [Pairwise comparison matrix (1 × 9) * Average weighted (9 × 1) of Normalization matrix]/Average score of the criteria from the Normalization matrix.

Table 6

Prioritization of projects

ProjectWeighted factorMISP1KHISNISRIP)KNLIS
Conveyance efficiency 0.3 
Application efficiency 0.21 
Soil type 0.15 
Average infiltration rate 0.11 
Final soil moisture 0.08 
Initial soil moisture 0.06 
Crop intensity 0.04 
Evapotranspiration 0.02 
Command area 0.02 
Prioritization percentage  65.62% 62.57% 60.08% 51.21% 69.92% 
ProjectWeighted factorMISP1KHISNISRIP)KNLIS
Conveyance efficiency 0.3 
Application efficiency 0.21 
Soil type 0.15 
Average infiltration rate 0.11 
Final soil moisture 0.08 
Initial soil moisture 0.06 
Crop intensity 0.04 
Evapotranspiration 0.02 
Command area 0.02 
Prioritization percentage  65.62% 62.57% 60.08% 51.21% 69.92% 

Note: The average score on the criteria for each project is presented in the table.

Weighted factor of criteria and their ranking

The weighted fraction of selected criteria is shown in Table 5. Efficient water utilization in the field is the main indicator of irrigation project performance and its impact on agricultural productivity. Consequently, conveyance and application efficiency are the key indicators for irrigation project selection. Studies show that about half of irrigation water could be lost through this process. Crop production increases exponentially with the increase in efficiency. Therefore, these criteria have high priority. Similarly, agricultural productivity depends on moisture content and infiltration capacity. Soil type, moisture content, and infiltration rate are strongly linked and control extra water losses in the field compared to efficiency. These criteria have a moderate weight for the irrigation project. Evapotranspiration is basically dependent on the meteorological characteristics of the command area that are out of human control. Increased evaporation reduces the project performance. Cropping intensity reflects farmers’ practices according to their needs, while the command area relates to land availability with respect to water availability. Based on expert judgment, these criteria have lower preferences compared to others. The result showed that conveyance efficiency (0.3) is identified as the most important criterion and ranked first, followed by water application efficiency (0.21) and soil type (0.15), respectively. The command area, with a weighted factor of 0.02 is identified as the least important criterion. These weights significantly influence the prioritization of the alternatives.

Prioritization of projects

Irrigation projects are prioritized as shown in Table 6. Priority is given to the project that scores more than 60%. The Kiran Nala Lift Irrigation Project (70%) was found to have higher priority, mainly due to its high conveyance and application efficiency, low evapotranspiration rate, and appropriate soil characteristics of the system compared to others. Conversely, the RIP (51%) has less priority. Other projects have good overall scores and can be chosen for operation and maintenance.

Among several methods, we employed the commonly used AHP method for the MCDM technique. The details of other methods can be found in Vassoney et al. (2021). Each method has its advantages and limitations. The reliability of the selected method depends on several factors. A biased opinion of an individual or a team member may distort the judgments, affecting the results (Saaty & Vargas 2022). Additionally, the variability in judgements may result in inconsistent outcomes.

The AHP is a data-extensive method; collecting data can be challenging to implement in developing countries with limited resources. The weights assigned for each criterion are often subjective, can introduce uncertainty, and affect the outcomes. Generally, the AHP method is well suited for small and simple projects due to the low number of criteria and alternatives involved.

We presented a novel approach to prioritize the irrigation projects in Nepal using a MCDM technique. This study addresses a critical gap in irrigation management by focusing on O&M prioritization with limited financial resources.

We conducted a comprehensive assessment of five irrigation projects in the Terai region: RIP, KNLIS, NIS, MISP1, and KHIS. These projects were evaluated using nine key criteria: conveyance efficiency, water application efficiency, soil type, infiltration rate, initial and final soil moisture contents, evapotranspiration, cropping pattern, and command area. These criteria were carefully selected based on their significant impact on irrigation performance and agricultural productivity.

In the AHP analysis, the formation of the comparison matrix, normalization matrix, and the obtained CR value (less than 10%) indicate that the assigned weights for each criterion are consistent. The analysis revealed that conveyance efficiency had the highest weighted factor (0.30), highlighting its critical role in irrigation performance, while the command area had the lowest weighted factor (0.02), signifying its relatively lesser influence.

Among the evaluated projects, the Kiran Nala Lift Irrigation Project was identified as the highest priority for operation and maintenance, scoring 70%. Despite its smaller command area, its efficient water use and minimal losses make it a strong candidate for investment. In contrast, the RIP was ranked as the lowest priority, scoring 51%.

Furthermore, conveyance efficiency (0.30) and water application efficiency (0.21) emerged as the most critical factors influencing irrigation project performance. Projects suffering from high infiltration losses and siltation require targeted interventions for rehabilitation to maximize their benefits. Conversely, the command area was found to have the least influence in the prioritization process.

This study presents a robust framework for prioritizing the irrigation projects in Nepal using the AHP method, emphasizing conveyance and application efficiency as key determinants of irrigation performance. By prioritizing projects based on efficiency and infrastructure health, policymakers and irrigation managers can allocate resources more effectively, enhancing decision-making for sustainable irrigation development.

The proposed methodology is adaptable to other irrigation systems facing similar challenges, ensuring optimal resource utilization in water-scarce regions. Additionally, this framework supports the prioritization of both ongoing and prospective projects while aiding in the O&M of the existing systems. Although this study focused on five projects and seventeen questionnaires, its approach remains applicable to a broader range of irrigation projects. Future studies may integrate additional socio-economic factors to refine project prioritization further.

The authors are thankful to the Department of Hydrology (DHM) for providing the daily precipitation and temperature data. The authors are grateful to the Water Resource Research and Development Centre (WRRDC) for sharing the data of the command area for rogation projects.

The authors declare that they have no known competing financial interests or personal relationships that have appeared to influence the work reported in this paper.

All relevant data are available from an online repository or repositories.

The authors declare there is no conflict.

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