International Journal of Agronomy

International Journal of Agronomy / 2020 / Article

Research Article | Open Access

Volume 2020 |Article ID 7065238 |

Humuri K. Haymale, Karoli N. Njau, Frederick C. Kahimba, "Estimating Conveyance Efficiency and Maize Productivity of Traditional Irrigation Systems in Usa River Catchment, Tanzania", International Journal of Agronomy, vol. 2020, Article ID 7065238, 11 pages, 2020.

Estimating Conveyance Efficiency and Maize Productivity of Traditional Irrigation Systems in Usa River Catchment, Tanzania

Academic Editor: Mathias N. Andersen
Received08 Feb 2020
Revised02 Jun 2020
Accepted23 Jun 2020
Published30 Jul 2020


Estimating the conveyance efficiency of traditional irrigation schemes systems is very important. It is because of understanding the volume of water lost along with the transportation facility, enhancing water usage and productivity, hence making better decisions about the utilization of water resources. The objective of the study was to determine water abstraction permit compliances and estimate conveyance efficiency and crop and water productivity of traditional irrigation systems in northern Tanzania. The task involved measurement of irrigation water flows to determine the amount of water abstraction, inflow (head) and outflow (tail) between the canals to determine the conveyance efficiency of the main, secondary, and tertiary canals of the traditional irrigation systems. Moreover, water and yield obtained at the farm level were determined. Results indicate that approximately of water transported reaches the destined farm which produced maize (Zea mays L) yields of , , and at downstream, midstream, and upstream which equals , , and , respectively, while about of water is lost along the canals through evaporation, seepage, and deep percolation and overtopping. Consequently, water measured at furrow intakes in total was , equal to more than the permitted amount of at Usa River Catchment. Interventions to minimize water losses starting at the furrow’s intakes are urgently required in the current trend of the increasing demand for water resources for food production and schemes performance. Subsequently, more effective conveyance technologies and water management strategies other than canal lining are required.

1. Introduction

Globally rain-fed agriculture’s contribution to food production is about ; the other is supplemented by irrigated agriculture [1]. However, irrigation consumes about of the available water [2]. Globally, approximately 277 million hectares of agricultural land is under irrigation (about of cultivated land), contributing of the food supplies with 2.3 higher yields compared to rain-fed agriculture as described by Adejumobi et al. [3]. Irrigation efficiency in Sub-Saharan Africa (SSA) was in the year 1998 and is expected to improve by by the year 2030 [1].

The SSA irrigated agriculture is said to use less than of the total renewable water resources to irrigate a land of six million hectares, which is equal to of the total irrigable land. Conversely, Asia region uses and Latin America uses of its total renewable water resources, which seem to be higher than SSA [1]. Utilization of water for irrigation needs a lot of attention in the catchment with scarce water resource. The performance indication of the irrigation schemes is revealed from the irrigation efficiency.

Generally, water from the source is being conveyed through different methods depending on the establishment of the scheme in terms of conveyance distribution and application system. Currently, the conveyance efficiencies for the traditional irrigation schemes in Tanzania range within for the main canal, for the secondary canal, and for a tertiary canal [4]. The different conveyance distribution facilities used include open lined canals, pipes, and earthen canals, which ensure water travel from the source to the farm field. It is believed that most water is being lost during distribution and application in the farm fields. However, conveyance efficiencies mainly relate to the engineering of the infrastructure, while the application efficiencies relate to farmer/agronomic practices [5]. Traditional irrigation schemes in the country rely on the runoff of the river abstraction and gravity flows with the irrigation infrastructures in the state of being temporal and poorly constructed and thus pose difficulty to water abstraction and overall water management, with low irrigation efficiencies. The conveyance efficiency of the irrigation schemes provides insight into the performance of the infrastructure and enhances water resource utilization. In the Usa River Catchment, the irrigation infrastructure is earthen traditional canals and does not have the capacity of holding and maintaining the intended quantity of water directed to the fields. Irrigation canal performance is part of the overall enactment of an irrigation area [6].

Tanzania has a total of 1,428 irrigation schemes where 1,328 are smallholders, 85 are private sectors, and 15 are government-owned [7]. The largest irrigation schemes are found in Kilimanjaro, Arusha, Morogoro, Iringa, and Mbeya [7]. Irrigated agriculture in Tanzania reportedly consumes approximately of the total water diverted, compared to domestic use and industrial water use [8]. Simultaneously, on-farm water use efficiency is typically very low, within , contributing to the heavy use of water for irrigation [8].

The conveyance efficiency normally dictates the amount of water to be delivered to the field, which depends on the characteristics of the channel. In the process of transporting water from the source to the farm/land, there is water loss through evaporation, transpiration, percolation, and spills. Consequently, the distance from the water source to the farmland, soil type, channel type and the slope of the channel are the other main causes of water losses.

A similar situation can also be found in the Usa River Catchment which is located in the Arusha region, near Arusha town. The catchment has about twenty (20) identified irrigation schemes that extract water from the rivers in the catchment (Figure 1). The catchment is water-stressed due to excessive withdrawal from surface and groundwater for irrigated farming of diverse crops.

However, no research has been conducted to understand the irrigation conveyance efficiencies and crop and water productivity in the Usa River Catchment. The efficiencies and productivity of the irrigation schemes remain a policy question for the basin water managers and decision-makers. There is a general assumption that some water can be released from the Usa Rivers to irrigation schemes. Similarly, it is not clear where to target such water-saving interventions.

Therefore, this study intended to estimate the conveyance efficiency and crop and water productivity in traditional irrigation schemes and irrigation practices in the Usa River Catchment where there are many farmers-managed irrigation schemes that the basin authority considers to have poor infrastructure, poor water management, and low yields.

2. Materials and Methods

2.1. Study Area Description

This study was carried out at the Usa River Catchment, within the Upper Pangani River Basin, North of Tanzania. The catchment is located within the northern region of Tanzania at to S and longitude to E (Figure 2). The catchment has an area of and forms part of the larger Kikuletwa Catchment. The catchment is located at the foot of Meru Mountain lying between Kikavu River Catchment running from Kilimanjaro Mountain and Nduruma River Catchment running from Meru Mountain. The rivers found within the catchment running from Meru Mountains include Malala, Tengeru, Usa River, Maji ya Chai, Mogadirisho, and Ngaresero, which discharge water in Kikuletwa River (Figure 2). The Usa River Catchment consists of administrative wards of Songoro, Nkoaranga, Maji ya Chai, Usa River, Kikwe, Seela, Singisi, and Poli. The largest plain area is found downstream of the catchment where the largest farms are located. The downstream of the catchment is at 914 m–1194 m, above-average mean sea level.

2.1.1. Topography of the Catchment

The topography of the Usa River Catchment is generally characterized by a slightly rolling plain from Mbuguni ward which steepens towards the foot of Meru Mountain where the rivers start. The average elevation is 1100 m above the mean sea level and the slope is dissected by the permanent, perennial, and seasonal rivers. Small springs are found in the middle part of the catchment which also recharges the rivers. The large area of the catchment is exhausted by anthropogenic activities like agriculture, pastoralists, and habitation. The land formation of the catchment is partly rocky, which is covered by the small layer of soil that supports the life of the living things and agricultural activities and partly is fertile soil. Moreover, the northern part of the catchment is where the Arusha National Park is located, which helps to recharge rivers due to the presence of forests. The hydrogeology of the catchment allows underground water movement as a result of recharging the available water resource and the soil reserving moisture for irrigation agriculture. Therefore, the area has great potential for irrigated agriculture due to the market demand for agricultural products to be supplied to the nearby populated City of Arusha.

2.2. Catchment Delineation and Intake Furrow Measurement

The catchment was delineated using ArcSwat Software from the Digital Elevation Model DEM of the area with a resolution of . The Digital Elevation Model was derived from the United States Geological Survey USGS data from 1995 to 2015 (Figure 2). Subsequently, irrigation water intakes (furrows) were located using coordinates taken by Garmin 60s GPS device (Figure 1) from upstream to the downstream followed by water intakes measurement using a current flow meter (SEBA Universal Meter F1 device with propeller 125 mm and pitch 300 mm). Additional data on the amount of water permitted per irrigation scheme was collected from the Pangani Basin Water Board Office (Table 1).

S/NFurrow namePermit no.Quantity permitted (L/s)Quantity measured (L/s)% of abstractionRiver sourceStatus intake

1Shamima14023620018995KikuletwaWith gate
2Star1406166870103KikuletwaWithout gate
3Mbukita14023720015176KikuletwaWithout gate
4Orbuso2285200215108KikuletwaWith gate
5TPL3156280.313046KikuletwaWith gate
6Mapama14055030024281KikuletwaWith gate
7Kammama140040200204102KikuletwaWith gate
8Valestika3727142.213091KikuletwaWithout gate
10Kwa Ugoro4761113.28150132KikuletwaWithout gate
11Dolly/BCW176584.96224264USAWith gate
12Kaanani111005520013568MalalaWithout gate
13Kitamaka14001420013869MalalaWith gate
14Elia1400462069345MalalaWithout gate
15Mkindi1400471008383Tengeruwith gate
16Ngolo14007100115115TengeruWithout gate
17Humalu111018075055110MalalaWithout gate
18Mimako14019185227267TengeruWith gate
19Furrow No.111101545100453453USAWithout gate
20Makiba3143198.24373188KikuletwaWithout gate

2.3. Conveyance Efficiency Determination

The flow measurement using current meter (SEBA Universal Meter F1 with propeller 125 mm and pitch 300 mm) device as shown in Figure 3 was carried out at every division point of the channel from the intake of the irrigation canal to the fields (Figure 4). The raw data were converted to flow rate (volume) using calibration formulae of the respective current meter impeller used. The difference between the inflow (head) and the outflow (end) of every segment was computed to determine the quantity of water lost in each of the segments as conveyance efficiency (Table 2). Furthermore, distances of one section of the channel were estimated using the GPS set to the distance calculation mode and walk along or near the section. The locations where the water flow measurements were taken at the intake (head), channel junctions (end/head), and the other point along the channel (end) are shown in Figure 4:where means quantity of water lost in a channel in L/s,   means quantity of water at the head (inflow) in L/s, and   means quantity of water at the end of channel (outflow) L/s.

Furrow nameCanal sectionDischarge extracted (L/s)Distance (m)Discharge loss (L/s)Discharge loss L/s/mLoss %Efficiency % (Ec)

ShamimaSection 11891051902840.04444.455.6
Section 28353891290.03335.564.5
StarSection 170411183290.02541.458.6
MbukitaSection 17253716190.02726.473.6
OrbusoSection 12091523648570.01627.372.7
Section 2100.59827330.0112.597.5
TPLSection 1153.3136.12251170.00811.288.8
MapamaSection 142916239242670.06862.337.7
KammamaSection 1223209864130.015694
Section 2196161202340.16817.582.5
Section 3817445470.0158.591.5
Section 471581148130.01118.881.2
ValestikaSection 1152872270650.02942.857.2
Section 24830873180.02137.562.5
KipilipiliSection 144729722281500.06733.566.5
Section 213212526270.027595
Section 35443.31109110.01020.479.6
Kwa UgoroSection 144882.531283650.11781.618.4
Section 246261781200.01143.156.9
Dolly/BCWSection 1257221.71357350.02613.686.4
Section 213212389890.0107.192.9
Section 381272546540.02166.833.2
KaananiSection 1198120.91457770.05338.861.2
Section 29919.7830790.09580.119.9
KitamakaSection 141392020.1004.995.1
EliaSection 1228672150.02265.434.6
MkindiSection 13733.934530.0099.190.9
NgoloSection 11431001215430.03530.169.9
HumaluSection 14840504.580.01616.783.3
Section 232246980.1162575
MimakoSection 1949063440.0064.495.6
Section 25848931100.01117.582.5
Section 3423546370.01516.783.3
Furrow no. 1Section 14404151452250.0175.794.3
Section 233533097550.0051.498.6
Section 33102711321390.03012.587.5
Section 48245531370.07045.154.9
MakibaSection 13732218461520.18040.859.2

Discharge loss in percentage (Q%) is as follows:where Qinflow is water quantity at the channel head (L/s) and Qoutflow is water quantity at the channel tail (L/s).

Conveyance efficiency (Ec) is as follows:

2.4. Crop Water Productivity Determination

In order for the crop plant to grow, water, soil, nutrient, and sunlight in terms of energy are needed. During their growth, plants tend to develop organic matter where in turn dry matter is obtained. During the data collection for crop water productivity, the pieces of lands of , , and size for downstream, midstream, and upstream, respectively, were identified. In our study, maize (Zea mays L) crop was selected because it is the staple food. Similarly, the irrigation schedule at every plot was monitored while the amount of water irrigated was measured using current meter and calculated. Subsequently, the produce from each plot was harvested, dried, and then weighed.

3. Results

3.1. Field Survey Result

During the field visit observation, twenty (20) furrow intakes were identified in the catchment (Figure 1). A number of furrow intakes were located at midstream and downstream of the catchment. Upstream of the catchment is steep and has small streams that accommodate the irrigation during the dry season.

3.2. Water Flow Measurements
3.2.1. Intakes

Many of the furrow intakes weirs were constructed using stones, sandbags, and tree logs (Figure 5), which do not catch water intended for irrigation and frequent maintenance. However, the weirs are provided for the purpose of directing water to the irrigation scheme and allowing fixing water gates for regulating irrigation water flow to meet the demand of a particular farm or scheme (Figure 6). Moreover, some of the furrow intakes were constructed using reinforced concrete but still do not work to the required form (Figure 6) while others were constructed locally using stones, tree logs, and sand buckets (Figure 5).

Furthermore, water diverted at the intakes was measured to see how much is withdrawn and how much is permitted to abstract (Table 1). Information on water use permit provided and amount of water permitted to abstract was collected from the Pangani Water Office. During the measurement of water flows at the intakes, it was discovered that some of the furrow intakes abstract more water relative to the allocated amount (Table 1).In that fact, water flows at the intakes exceeded the permitted amount because the irrigation water demand of respective scheme is high or because of the issue of regulating structure that controls the amount of water to flow. The issue of monitoring the diverted water to ensure that it complies with water use permit granted to the Water User Association (WUA) is a problem within the catchment. The water irrigation furrow intakes were scattered from upstream to the downstream; however, after the river confluence going downwards there are many accumulated furrow intakes due to favoring landforms and availability of land for farming (Figure 1).

3.2.2. Irrigation Conveyance Infrastructure

The Usa River Catchment irrigation scheme’s main canals, secondary, and tertiary were earthen which transport water from the intake to the scheme. The irrigation infrastructure system found in the catchment can be represented in a tree form. The main stem taps water from the soil and transports it to the branches. The branches supply the twigs with water and finally it enters into the leaves, where it will either be used by the plants for growth or be lost into the air through evaporation.

The same can be seen in Usa River Catchment traditional irrigation schemes infrastructure where main/primary canal (stem) taps water from the river and then it is distributed by the smaller secondary canal (branches) to the tertiary canal (twigs), which are smaller, and enters into the fields (Figure 4). According to the study conducted in the catchment, water losses at the canals were on average (Table 2). Further, traditional irrigation does abstract water from the source after being given water permit and conveys the same using earth canal to the farm. Moreover, the distributing structure like junction, turnout boxes, and the gate valve farmer uses traditional materials like stone, soils/earth, and tree logs.

The same can be seen in Usa River Catchment traditional irrigation schemes infrastructure where main/primary canal (stem) taps water from the river and then it is distributed by the smaller secondary canal (branches) to the tertiary canal (twigs), which are smaller, and enters into the farm (Figure 4). According to the study conducted in the catchment, it is shown that water losses at the canals were on average of (Table 2). Further, traditional irrigation does abstract water from the source locally and conveys the same using earth canal to the farm. Moreover, the distributing structure like junction, turnout boxes, and the gate valve farmer uses traditional material like stone, soils/earth, and tree logs

3.3. Water Abstraction Compliances and Distributions

About twenty (20) irrigation furrow intakes are owned by the farmer groups called Water User Associations (WUA). The main objectives of forming Water User Association are to manage sustainably water resource in their area, to educate and advise water uses and productivity, to resolve water conflict, for participatory management of water resource and environment, and to identify new members [9]. Each furrow intake has a management team which is called the furrow committee that is responsible for the distribution and allocation of water to its members during the dry periods. The leaders normally got problems where they were being blamed by irrigators that they do not allocate water equally and fairly. This was revealed after water flow measurement at the intakes where twelve (12) out of twenty (20) furrow intakes, which is equal to , abstract more water relative to the granted permits (Table 1). The data explains that reasons are due to unavailable control and regulating structures or being subject to operational management on water allocation for irrigation in a particular furrow. This is true at the catchment because Water User Association (WUA) called “UWAMAKIJU” committee meets once every week discussing issues of water allocation and distribution, resolving conflict, and coming up with a resolution as per articles of association of “UWAMAKIJU” during the dry season. In this research, an irrigation infrastructure has shown inefficiency of water supply controls at the intake, because the diverted water from the source/intake is higher than the discharged amount to the farm (Table 1).

3.4. Results of Crop Water Productivity

The catchment was divided into three agroecological zones: upstream, midstream, and downstream. In each zone, the crop and water productivity were calculated and showed variation in values. Under normal circumstances, every zone has got its constraints of crop production. Table 3 describes that total volumes of water of , , and for , , and at downstream, midstream, and upstream, respectively, were used. Similarly, yields of , , and , equal to crop productivity of , , and , were harvested per season.

ZonesIrrigation scheduleWater (L/s)Time (hrs)Volume (m3)Size of farm (ha)Yield (kg)Water productivity (kg/m3)Crop productivity (kg/ha)




4. Discussion

4.1. Water Conveyances, Losses, and Efficiency

The obtained results were analyzed using R-program and found that the correlation between distance and the loss of water in the canal is more significant since the value is less than 0.05 ( > 4.61e−06) (Figure 7). As the length of the irrigation channel increases, it escalates the water loss on channel, hence low conveyance efficiency (Figure 8). Subsequently, the relationship of the water losses and efficiency is mutual because when water is lost along the channels, this affects the efficiency of conveyance and vice versa (Figure 9). The phenomena of water losses are caused by temporal channels, earthen traditional canals, and insufficient size to hold a quantity of water, inefficient monitoring, and poor irrigation water management. In practice, farmers need water for irrigation while engineers and economists need the amount of water for irrigation to be realized in terms of technical efficiency and productivity.

4.2. Management of Traditional Irrigation Systems

The poverty alleviation is associated with development of irrigation infrastructure and agricultural water management and promotes welfare of rural community and economic growth by increasing agricultural production and productivity [10, 11]. The farmers cultivate crops based on food and market need, but water is allocated as per schedule agreed. Administrator and policy-makers should insist on good practices and water use efficiency to enhance sustainability of water resource and irrigation agriculture. However, the government policies and international partners in irrigation emphasize water uses efficiencies, good agricultural practice (GAP), and sustainable water practices in irrigation systems by improving infrastructure and introducing new technology in line with irrigation scheduling to “gain efficiency” [12, 13]. Substantial decrease of water from the sources creates pressure on stakeholders and hence raises awareness for irrigation water use. Conveniently, to satisfy the future water demand for irrigation agriculture, infrastructure improvement and water management from source and at the farm field are of vital importance. The fragmented management system and weak involvement of stakeholders exacerbated irrigation water management hence amplifying inefficiency of water resources utilization [14].

4.2.1. Compliances to Permitted Water Quantities

According to the field survey, irrigation agriculture withdraws out of a permitted amount of (Table 1); however, catchment consists of several rivers that collect water from the catchment covering an area of having rivers Tengeru, Malala, Maji ya Chai, Usa River, and Kikuletwa. The furrow intakes are distributed throughout the catchment from downstream to the upstream (Figure 1). However, the water abstraction is managed from Basin Water Offices (BWOs) through the water management act of 2009, Section 23 (a)(b), Section 31(2), and National Water Policy 2002 [15, 16]. But the water allocation is a difficult activity because it involves two sides that are water users and policy-makers. However, planning and decision-making are supposed to be participatory, involving all stakeholders stated in the National Water Policy of 2002, Section 3.1 (iv). Different amount of water from the river’s source is withdrawn in each furrow during the season of irrigation (Figure 10) and distributed among the members at furrow level. However, the management of water flows at the intakes was inefficient because more water is withdrawn relative to the permitted amount (Table 1). In this research, an irrigation infrastructure has shown inefficient water supply at the intake, because the diverted water from the source/intake is higher than the permitted amount for irrigation due to headworks malfunctioning (Table 1).

Further, abstracting much water from the river source reduces the share of the downstream water user and environmental flow and creates pressure on the catchment. Despite its importance to our lives and irrigation development, water is unevenly distributed in time, space, and quantity and is with great variations in quality. Some areas get more water than they need while others are suffering from water shortage. When there is water scarcity, food security is threatened and production of energy becomes difficult, affecting economic activity, posing a threat to environmental integrity, and creating water conflicts between the water users [17]. The fragmented planning between the water stakeholders aggravates the issue of water resource utilization making it more difficult. Additionally, the balance of water available in the river sources is not well known due to flow variation, recharge capacity which is subject to weather, and unavailable gauging stations. According to the analysis, the linear relationship of the discharge permitted from the water office and the discharge measured at the intake is not significant (Figure 11). Furthermore, the trend has also shown that as the water office grants more water permits, the enforcement in the water management and water control should be improved.

4.2.2. Management of the Irrigation Infrastructure System

The water supply for irrigation aims to be used for crop production which involves conveying water from the source. Water losses in conveyances reduce water diverted while echoing to increase crop productivity to meet the increasing world population remains a challenge [18]. Using more precise water delivery practices gives water managers more flexibility to deliver water where it is needed and when it is needed [19]. Simultaneously, the scattered schemes and positioning away from the irrigation scheme from the water source are one of the barriers to conveyance efficiency as illustrated in Table 2. Consequently, irrigation water demand is increasing globally over time with population increase, for rising income and changes in dietary preference [20]. Conveniently, to satisfy the future water demand for irrigation agriculture, infrastructure improvement and water management from source to farm field are of vital importance. Eventually, more than 850 million out of more than 1 billion are the rural poor people living on less than 1$ a day depending on irrigation agriculture [11]. In the context of agroecological zones, the water competition is increasing across due to demand changes caused by population increase and climate change effect [21]. Much of the investment is needed to improve and adapt existing irrigation infrastructure systems in areas already very reliant on intensively irrigated agriculture [22] that run from upstream to the downstream across an agroecological zone of the catchment. Investing in irrigation agriculture and water management is very important because of the debate on climate change, population growth, and food security [23]. The sustainability of irrigation agriculture in terms of irrigation water supply for food production and environment uses in a catchment in question needs reliable irrigation headwork, proper and modern conveyances, application efficiency in the field, and water management enforcement. Further, access to irrigation infrastructure reduces the incidence of poverty, and upgrading watercourse saves water which results in higher cropping intensity, higher crop productivity, greater food security, and improved farm incomes [23].

4.2.3. Water Use and Crop Water Productivity

Table 3 indicates that amount of water applied for irrigation was , , and with yield of (), (), and () at downstream, midstream, and upstream, respectively, in one season; however an average conveyance efficiency is . At the crop level, water productivity (WP) can be defined as the ratio of biomass with economic value (for example, grain yield of cereals) over amount of water transpired (WPt) [24]. Moreover, Kijne et al. [25] defined water productivity (WP) as a measure of the ability of agricultural systems to convert water into food. Similarly, Cook et al. [26] also defined as measure of output from a given agricultural system in relation to water it consumes, which can be measured in portion or entire system. Based on the review done by Zwart and Bastiaanssen [27] and Yazar et al. [28], globally crop water productivity for maize (Zea mays L) ranges from to while in this research, it ranges from to . Furthermore, in the field experimental research on traditional irrigation scheme by Igbadun et al. [29], the crop water productivity of maize (Zea mays L) at Mkonji Subcatchment of Great Ruaha River Basin obtained ranges from to for the applied water. Following the results of our research and the other researchers regarding the CWP, traditional irrigation schemes have low crop water productivity, which therefore needs improvement in irrigation water management, traditional infrastructure, and water application in the field.

5. Conclusion and Recommendations

The traditional irrigation system in the catchment needs improvements of water utilization for easy and sustainable management of water for irrigation and enhanced agricultural crop productivity. The proper and designed infrastructure of the irrigation schemes contributes to reliable water allocation and efficient water supply to the destined command area. However, Usa River Catchment (URC) traditional irrigation schemes infrastructure system contains various constraints at the institutional and local level of utilization of this scarce water resource. These include water allocation, distribution, irrigation scheduling and maintenance of water channel, weak stakeholders involvement, and indifference in local and central administration. The provision of these administrative infrastructures and agronomy in the system will improve the provision of irrigation water supply services in the catchment which will be reliable and efficient. This measure will bring a positive effect to the irrigation water supply and allocation in the basins’ irrigation schemes. Subsequently, water flow measurement structures are also needed to ascertain the quantity of water committed to the scheme by water office. Furthermore, land for irrigation should be monitored by keeping the farm size at a selected fertile area so that water could not be lost unnecessarily in irrigation conveyances and at farm field applications. This is important for the catchment to utilize the water resource in irrigated agriculture, water for environmental flows, and ecosystem uses by providing basin water resource management plan based on water balance, water demand, and requirement of the reserve [16]. Similarly, controlling water abstraction from the sources and illegal water abstraction as stipulated in the water policy of 2002 and the water resource management act of 2009 [16] should be enforced. Besides, the new technology of irrigation system should be introduced in the catchment for sustainability of agricultural irrigation and water resource utilization. Similarly, irrigators’ involvement in water management and advising them on high value crop cultivation, water serving irrigation practices, and perpetual water flow measurement for records and decision-making on water allocation at scheme level up to the water office and decision-makers is of great importance.

Data Availability

The data can be made available upon request.

Conflicts of Interest

The authors declare that there are no conflicts of interest regarding this paper.


The authors thank the Nelson Mandela African Institution of Science and Technology and Arusha Technical College for their support.


  1. E. Clay, Food Security: Concepts and Measurement. Trade Reforms and Food Security: Conceptualising the Linkages, FAO, Rome, Italy, 2002.
  2. GWP. Integrated Water Resources Management. Technical Report 4, Techical Advisory Commettee, 2000.
  3. M. Adejumobi, J. Ojediran, and O. Olabiyi, “Effects of irrigation practices on some soil chemical properties on omi irrigation scheme,” International Journal Engineering Research and Applications, vol. 4, no. 10, pp. 29–35, 2014. View at: Google Scholar
  4. U.R.Tanzania. New Directions for Irrigation Development in Tanzania. The Context of Public Private Partnershi’p. Technical report, Ministry of Finance, Water and Irrigation and National Irrigation Commission, 2016.
  5. G. E. Van Halsema and L. Vincent, “Efficiency and productivity terms for water management: a matter of contextual relativism versus general absolutism,” Agricultural Water Management, vol. 108, pp. 9–15, 2012. View at: Publisher Site | Google Scholar
  6. S. Kisnanto, R. Hadiani, and C. Ikhsan, “Infrastructure performance of irrigation canal to irrigation efficiency of irrigation area of candi limo in Mojokerto district,” IOP Conference Series: Materials Science and Engineering, vol. 333, p. 12096, 2018. View at: Google Scholar
  7. U. R. Tanzania, District Irrigation and Water Harvesting Support (Mainland). Support to NEPAD-CAADP Implementation TCP/URT/2908(I), Ministry of Agriculture and Irrigation, Dar es Salaam, Tanzania, 2005.
  8. U. R. Tanzania, “National water sector development 2006–2015,” Technical report, Ministry of Water and Irrigation, Beijing, China, 2008. View at: Google Scholar
  9. U. R. Tanzania, “National water policy,” in Water Policy, pp. 1–49, International Water Stewardship Programme, Eschborn, Germany, 2002. View at: Google Scholar
  10. S. T. Intizar Hussain, M. A. Hanjra and D. Wijerathna. Impact of Irrigation Infrastructure Development on Dynamics of Incomes and Poverty Econometric Evidence Using Panel Data from Sri Lanka. Technical report, International Water Management Institute (IWMI) and Japan Bank for Interantional Cooperation (JBIC) 2003.
  11. R. E. Namara, M. A. Hanjra, G. E. Castillo, H. M. Ravnborg, L. Smith, and B. Van Koppen, “Agricultural water management and poverty linkages,” Agricultural Water Management, vol. 97, no. 4, pp. 520–527, 2010. View at: Publisher Site | Google Scholar
  12. F. Behnsen, “Sustainable water management in Usa river,” International Water Stewardship Programme, pp. 1-2, 2017. View at: Google Scholar
  13. R. Boelens and J. Vos, “The danger of naturalizing water policy concepts: water productivity and efficiency discourses from field irrigation to virtual water trade,” Agricultural Water Management, vol. 108, pp. 16–26, 2012. View at: Publisher Site | Google Scholar
  14. K. Laoubi and M. Yamao, “Management of irrigation schemes in Algeria: an assessment of water policy impact and perspectives on development,” WIT Transactions on Ecology and the Environment, vol. 125, pp. 503–514, 2009. View at: Google Scholar
  15. U. R. Tanzania, “National water policy,” Water Policy, 2000. View at: Google Scholar
  16. U.R. Tanzania. Performance Audit Report on the Control of Water Abstraction from the Water Sources. Technical report, Ministry of Water and Irrigation Through Basins Water Boards, March 2017.
  17. D. R. Bennett, R. V. Riewe, T. Entz, and S. A. Woods, “Water conveyance and on-farm irrigation system efficiency gains in southern alberta irrigation districts from 1999 to 2012,” Canadian Water Resources Journal/Revue canadienne des ressources hydriques, vol. 40, no. 2, pp. 173–186, 2015. View at: Publisher Site | Google Scholar
  18. A. J. Clemmens and D. J. Molden, “Water uses and productivity of irrigation systems,” Irrigation Science, vol. 25, no. 3, pp. 247–261, 2007. View at: Publisher Site | Google Scholar
  19. L. Chapala, “Water use and productivity in a river basin,” Water, vol. 21, no. 5, pp. 278–310, 2000. View at: Google Scholar
  20. C. De Fraiture and D. Wichelns, “Satisfying future water demands for agriculture,” Agricultural Water Management, vol. 97, no. 4, pp. 502–511, 2010. View at: Publisher Site | Google Scholar
  21. E. Akkuzu, H. B. Ünal, and B. S. Karataş, “Determination of water conveyance loss in the menemen open canal irrigation network,” Turkish Journal of Agriculture and Forestry, vol. 31, no. 1, pp. 11–22, 2007. View at: Google Scholar
  22. H. Turral, M. Svendsen, and J. M. Faures, “Investing in irrigation: reviewing the past and looking to the future,” Agricultural Water Management, vol. 97, no. 4, pp. 551–560, 2010. View at: Publisher Site | Google Scholar
  23. F. A. Ward, “Financing irrigation water management and infrastructure: a review,” International Journal of Water Resources Development, vol. 26, no. 3, pp. 321–349, 2010. View at: Publisher Site | Google Scholar
  24. B. Bouman, “A conceptual framework for the improvement of crop water productivity at different spatial scales,” Agricultural Systems, vol. 93, no. 1-3, pp. 43–60, 2007. View at: Publisher Site | Google Scholar
  25. J. W. Kijne, R. Barker, and D. J. Molden, Water Productivity in Agriculture: Limits and Opportunities for Improvement, Cabi, Wallingford, UK, 2003.
  26. S. Cook, F. Gichuki, and H. Turral, “Water productivity: estimation at plot, farm and basin scale,” CIAT, Cali, Colombia, 2006. View at: Google Scholar
  27. S. J. Zwart and W. G. M. Bastiaanssen, “Review of measured crop water productivity values for irrigated wheat, rice, cotton and maize,” Agricultural Water Management, vol. 69, no. 2, pp. 115–133, 2004. View at: Publisher Site | Google Scholar
  28. A. Yazar, F. Gökçel, and M. Sezen, “Corn yield response to partial rootzone drying and deficit irrigation strategies applied with drip system,” Plant, Soil and Environment, vol. 55, no. 11, pp. 494–503, 2009. View at: Publisher Site | Google Scholar
  29. H. E. Igbadun, H. F. Mahoo, A. K. Tarimo, and B. A. Salim, “Crop water productivity of an irrigated maize crop in mkoji sub-catchment of the great ruaha river basin, Tanzania,” Agricultural Water Management, vol. 85, no. 1-2, pp. 141–150, 2006. View at: Publisher Site | Google Scholar

Copyright © 2020 Humuri K. Haymale et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

More related articles

 PDF Download Citation Citation
 Download other formatsMore
 Order printed copiesOrder

Related articles

Article of the Year Award: Outstanding research contributions of 2020, as selected by our Chief Editors. Read the winning articles.