Introduction
Irrigation is the top heavy user of freshwater resources globally. More than 70% the freshwater abstraction from water bodies and 90% of the consumptive use of fresh water is due to irrigated agriculture (FAO, 2015; Grafton, Williams and Jiang, 2017; Zhou et al., 2020). In addition, the demand for irrigation water is increasing associated with the ever increasing demand for food and fiber which in turn are due to growing population and expanding market. On the other hand, the irrigation requirement is also increasing at global scale due to global warming (Grafton, Williams and Jiang, 2017; Zhou et al., 2020; Gabr and Fattouh, 2021; Haile et al., 2024). Furthermore, the amount of fresh water globally available for different uses is becoming more uncertain due to climate change. Under these conditions, improving water management in irrigation systems can greatly contribute in mitigating the global challenges in addition to addressing water management issues locally. Improved irrigation water management is crucial in order to address the global and local water issues.
Improved irrigation water management mainly focuses on saving and conserving water resources. Accordingly, the main focus is reducing the irrigation water needs through different options (Abdelhafid, Gharb and Maarouf, 2022). The improved water management can also be aimed to achieve optimal crop yield, and reduced the risk of water logging and salinization. One of the most important management option in irrigation water management is irrigation scheduling. Irrigation scheduling is the process to determine the amount and frequency of irrigation water application in the field. It can help to reduce the disproportion between water demand and supply, to improve crop yield, reduce risk of water logging and salinization, and there by ensure sustainability of irrigated farms. Irrigation scheduling can optimize crop yield by avoiding under or over irrigation, improve water use efficiency, so saves water and contributes to sustainable water resources management, reduces cost of irrigation especially by avoiding over irrigation, and ensure sustainability of irrigation land by avoiding water logging and salinization problems (Clemmens and Molden, 2007; Etissa et al., 2014; Wabela et al., 2022; Bekele et al., 2024).
In Ethiopia, irrigation development is at nascent stage. More than 85% of total Ethiopian population is heavily dependent on rain feed agriculture. The country is facing frequent and severe devastating droughts despite its huge potential surface and subsurface water resources. Most of the irrigation development in Ethiopia is concentrated in Awash River basin. However, the major surface water resources of the country resides in the Abay (the Blue Nile) River basin.
The basin is the biggest river basin accounting to more than 44% of the surface water resource potential of Ethiopia. The Abay River contributes to more than 62% for the flow of River Nile, the other two rivers add up the remaining share to the total contribution of more than 86 to the flow of Nile. The irrigation potential of the basin is estimated as 815,581 hectares (21.8 % of the total national irrigation potential) (Awulachew et al., 2007; Awlachew, 2010). Yet, there are very few irrigation schemes in Abay River basin. As the result, large majority of rural population in the basin is suffering from lack or absence of irrigation development.
Fincha sugar estate is among the very few irrigation schemes in the Abay basin. The scheme was initiated in 1988 as state farm for production of cereal crops but changed to sugar plantation starting from 1999. The estate uses sprinkler irrigation for its entire sugarcane plantation of around 19,602.6 hectares. The use of such high efficiency irrigation system shows the positive roles the country is playing for improved water management and sustainable use of the Nile water resources. This can be considered exemplary to the downstream countries in the basin, mainly to Egypt which remained reluctant to improve its water resource management and supplement the surface water resources with alternative sources. In Fincha sugar estate, fixed predetermined irrigation schedule was practiced for several years at least until 2002. This schedule consists of the depth and interval of irrigation that are unchanging for all soils, growth stage, and seasons. Accordingly, the sprinkler heads are set at a particular position for 24 hours of operation and returning back to this position at 15 days interval. The operation and maintenance manual by Booker Tate (1998) suggested the use of fixed irrigation schedule only until the irrigation personals get well experienced with operation of the system. The practice could cause over-irrigation for younger growth stages, moisture stress for lighter and shallower soils, especially in dry months and older growth stages, and lower application efficiency for heavy clay soils due to smaller irrigation intervals than required. However, it took several years before the practice was considered for revision. The estate started reconsidering the practice following research recommendation in 2002. The recommendation was to revise the existing fixed schedule and replace it with predetermined irrigation schedule varying with crop stage, soil type, and months of the year (Habib, 2002). The recommendation was based on calculation of irrigation schedules, did not show the impacts on yield and water efficiency. In addition, some schedules are difficult to apply with in the design capability and flexibility of the system and working hours. However, the sugar estate started revising the practice based on subjective assessments.
For instance, the field irrigation interval was increased in black cotton soils. In addition, the estate attempted to vary application depths, trying 12 hours and 6 hours set times. These actions are advantageous in increasing irrigation speed / reduce irrigation period in the given field. This could give more water of required pressure in adjacent and remote fields where irrigation has to go on. However, the estate faced some challenges on applicability of 6 hours set time as it requires night-time shifting of sprinkler positions, making it difficult for field irrigation personnel and field supervisors.
The sugar estate has continued to select and apply more flexible schedule based on subjective assessment. However, the impacts of the revised practices on yield and water efficiency remained unknown. Thus, while it is very impressive to see such progressive adjustment in irrigation scheduling practices under the complex conditions, it is clear that the decisions should be based on empirical evidence of possible impact of irrigation schedules. At least empirical evidence related to the impacts different irrigation schedules on crop yield, and water efficiency need to be made available for the estate be able to make to make informed decision.
The effect of different scheduling scenario are normally evaluated through experimental research under specific local conditions. However, crop models can also provide fairly reliable results with minimal cost and time. It is known that modelling and simulations have great benefit to represent and analyse large number of scenarios in short time and easily which are often costly and difficult to manage even under complex experimental designs. One of the most widely used and effective crop model is CROPWAT (Karuku et al., 2014; Surendran et al., 2015; Kumari, 2017; Moseki, Murray-Hudson and Kashe, 2019; Gabr and Fattouh, 2021; Reta, Hatiye and Finsa, 2024). Local study in Ethiopia shows that CROPWAT is more than 96% efficient in estimation of yield reduction compared with results from field experimentation (Etissa et al., 2014). Another study has recommended use of CROPWAT for irrigation scheduling to achieve more efficient water use and better crop yield at Fincha sugar estate (Geleta, 2019). Therefore, CROPWAT model is used in this study to identify feasible irrigation schedules for sprinkler irrigation system of Fincha sugar estate.