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Productivity analysis of the Río Bravo irrigation districts using performance indicators
Mauro Íñiguez-Covarrubias; Waldo Ojeda-Bustamante; Víctor Manuel Olmedo-Vázquez
Mauro Íñiguez-Covarrubias; Waldo Ojeda-Bustamante; Víctor Manuel Olmedo-Vázquez
Productivity analysis of the Río Bravo irrigation districts using performance indicators
Análisis productivo de los distritos de riego del Río Bravo usando indicadores de desempeño
Ingeniería agrícola y biosistemas, vol. 12, no. 2, pp. 131-158, 2020
Universidad Autónoma Chapingo
resúmenes
secciones
referencias
imágenes

Abstract

Introduction: Irrigation districts (IDs) are irrigation projects that require periodic evaluation to determine performance.

Objectives: To analyze the production behavior of several IDs located in the transboundary Río Bravo basin, Mexico.

Methodology: Agricultural and hydrometric information was compiled, organized and analyzed for 11 IDs in the Río Bravo basin to determine production performance based on seven indicators.

Results: The production value with respect to the volume of water extracted from the supply source varied from 1.1 to 9 $·m-3, while the productivity of water extracted from the supply source varied from 0.6 a 5.7 kg·m-3 and the production per unit of water delivered to users varied from 0.81 to 9.27 kg·m-3.

Limitations of the study: Performance indicators reflect the productivity of the irrigation area according to management of the crop, irrigation service, technological package, crop pattern, infrastructure, among other factors.

Originality: Performance of IDs located in the high-water pressure area in the Río Bravo basin was analyzed based on available information.

Conclusions: Several performance indicators are required to characterize integrally IDs’ productivity, With the use of hydro-agricultural indicators it is possible to implement improvement actions, where the value of irrigation water can be maximized for the benefit of producers.

Keywords: productivity indices, conduction efficiencies, evaluation of irrigation areas.

Resumen

Introducción: Los distritos de riego (DR) son proyectos de irrigación que requieren ser evaluados periódicamente para determinar su desempeño.

Objetivos: Analizar el comportamiento productivo de varios DR localizados en la cuenca transfronteriza del Río Bravo, México.

Metodología: Se compiló, organizó y analizó información agrícola e hidrométrica de 11 DR de la cuenca del Río Bravo para determinar su desempeño productivo a partir de siete indicadores.

Resultados: El valor de la producción con respecto al volumen de agua extraída de la fuente de abastecimiento varió de 1.1 a 9 $·m-3, mientras que la productividad del agua extraída de la fuente de abastecimiento varió de 0.6 a 5.7 kg·m-3 y la producción por unidad de agua entregada a usuarios fue de 0.81 a 9.27 kg·m-3.

Limitaciones del estudio: Los indicadores de desempeño reflejan la productividad de la zona de riego de acuerdo con el manejo del cultivo, servicio de riego, paquete tecnológico, padrón de cultivos, infraestructura, entre otros factores.

Originalidad: Con base en la información disponible, se analizó el desempeño de los DR localizados en la zona de alta presión hídrica de la cuenca del Río Bravo.

Conclusiones: Para poder caracterizar la productividad de los DR en forma integral, se requieren varios indicadores de desempeño. Con el uso de indicadores hidroagrícolas es posible plantear acciones de mejora, en donde se pueda maximizar el valor del agua de riego en beneficio de los productores.

Palabras clave: indicadores productivos, eficiencias de conducción, evaluación de zonas de riego.

Carátula del artículo

Scientific article

Productivity analysis of the Río Bravo irrigation districts using performance indicators

Análisis productivo de los distritos de riego del Río Bravo usando indicadores de desempeño

Mauro Íñiguez-Covarrubias
Instituto Mexicano de Tecnología del Agua, Mexico
Waldo Ojeda-Bustamante
Colegio Mexicano de Ingenieros en Irrigación, MÉXICO
Víctor Manuel Olmedo-Vázquez
Universidad Autónoma Chapingo, Mexico
Ingeniería agrícola y biosistemas, vol. 12, no. 2, pp. 131-158, 2020
Universidad Autónoma Chapingo

Received: 24 October 2018

Accepted: 13 May 2020

Introduction

In Mexico, irrigation districts (IDs), consisting of a delimited irrigation area, are irrigation projects established by the Federal Government through presidential decrees, since 1926, the year in which the Comisión Nacional de Irrigación was founded. IDs were created to promote national agricultural production and to ensure commercial production in times of limited or scarce rainfall.

IDs have been managed, operated and maintained by the Federal Government since creation. At the beginning of 1992, the centralized federal administration, through the Comisión Nacional del Agua (CONAGUA), transferred the administration of minor distribution network and the users irrigation service through Water Users Associations (ACUs, for its acronym in Spanish), and issued the water concession rights, as well as the use of hydraulic infrastructure works. Currently, the organization of an ID is mixed, because it involves the CONAGUA, the ACUs and a Federation of ACUs known as Limited Responsibility Society (S. de R. L., for its acronym in Spanish). The ACUs are responsible for the operation, conservation, and management of the infrastructure under concession to provide the irrigation service to the users. The water delivery responsibility from the source to the farm intake are as follow: from the CONAGUA to the S. de R. L., from the S. de R. L to the ACUs and from the ACUs to the users (Palacios-Vélez, 2000).

Irrigated agriculture requires various techniques for the farm irrigation application once water service is delivered to the ID users. This type of agriculture demands large capital investments and frequent maintenance of hydraulic infrastructure: dams, canals, and conduction, distribution and protection structures (CONAGUA, 1994).

The analysis of performance indicators for irrigation areas requires statistical tools. Infante-Gil and Zárate-de Lara (2012) show elements of descriptive statistics and statistical inference that can be used to generate and analyze performance indicators. The productivity of an irrigated area may indirectly indicate the capacity of the irrigation infrastructure to generate the planned products and the level at which the available resources or inputs are used. The better the productivity, the higher the profitability of the ID. In this way, optimal resource management seeks to ensure that every organization manages to improve productivity with the available infrastructure and resources.

The analysis of performance indicators through benchmarking applied to irrigation areas has been documented by Burt and Styles (2004) and Malano, Burton, and Makin (2004). This technique has been used to compare the water management performance of ACUs in various countries around the world (Alexander & Potter, 2004; Cakmak, Beyribey, Yildirim, & Kodal, 2004; Ruiz-Carmona, Ojeda-Bustamante, & Contijoch, 2006). Altamirano-Aguilar et al. (2017) classified and evaluated Mexico's IDs based on performance indicators, for which they grouped IDs into clusters by climate group. In this study they classified the IDs located in the Río Bravo basin, which are contemplated in the dry group in the "Water Treaty" of 1944 between Mexico and the United States of America (Mexico-USA). In the case of Bajo Río Bravo ID 025 and Bajo Río San Juan ID 026, which are located in the Bajo Bravo sub-region, Altamirano-Aguilar et al. (2017) mentioned that they belong to another climate group and, in general, the irrigation performance of all the conglomerates was reported as low.

Olmedo-Vázquez, Camacho-Poyato, Rodríguez-Díaz, Minjares-Lugo, and Hernández-Hernández (2017) analyzed irrigation water use management in ACUs of ID 041, Río Yaqui, Mexico, based on eleven yield indicators and eight productivity efficiency indicators. These authors reported that most of the ACUs were inefficient (66%) in the four agricultural years analyzed, from 2010 to 2014.

According to the dictionary of the Royal Spanish Academy (RAE in Spanish), productivity is a concept that describes the capacity or level of production per unit of input. In economics, productivity is understood as the link between what has been produced and the means used to achieve it (labor, materials, energy, among others), and is usually associated with efficiency and time: the less time invested in achieving the expected result, the greater the production character or performance of the system (Blanchard, 2017).

Since water is a scarce resource, water use efficiency is a concept of productivity at the biological level to describe the amount of biomass accumulated (yield) as a function of the volume of water supplied (Bos, Burton, & Molden, 2005). If this term is applied to irrigated agriculture, it can be expressed in terms of yield (kg·m-3) or in economic terms regarding the unit of volume of water applied ($·m-3).

The overall conduction efficiency of an ID (m3·m-3) is given by the total volume of water delivered (m3) to users at farm intake level among the total volume of water withdrawn (m3) from supply sources (surface + groundwater). Intrinsically included in this relationship of volumes is the method of water distribution, infrastructure and regulation systems (Íñiguez-Covarrubias, de León-Mojarro, Prado-Hernández, & Rendón-Pimentel, 2007). On the other hand, the total volume of water extracted from the source of supply by irrigated area (m3·ha-1) integrates the crop water needs, farm efficiency and global conduction efficiency, being an important parameter in the water resources management of an ID.

The Secretaría de Recursos Hidráulicos (SRH, 1973), in the recommendations of the “Project Manual of Irrigation Areas”, defined the global efficiency of an ID (Edist) as the product of conduction efficiency (Econd) and farm efficiency (Eparc), for which a conduction efficiency is determined according to the type of canal lining: soil (Econd=0.7), masonry (Econd=0.75) or concrete (Econd=0.85). On the other hand, the term productivity is related to yield, since it requires good management of resources in order to achieve results that make the work carried out within the association efficient, both in the provision of the service and in the methods used and the internal relationship of the organization.

The concepts and variables associated with the main indicators for evaluating the management, planning, operation and conservation behavior of large irrigation areas are found in the study of Bos et al. (2005) By conducting an analysis of production indicators, it is possible to lay the groundwork for subsequent studies, this in order to update the indicators so that they can quantify changes in the performance of IDs in response to policies, programs, climate patterns or management of an irrigation area. In this sense, the objective of this study is to quantify and analyze the behavior of productive performance indicators of 11 IDs located in the Río Bravo basin, México.

Materials and methods

Figure 1 shows the study region, which is the production area of the IDs located in the transboundary Río Bravo basin, Mexico, bordering the USA.


Figure 1
Location of the irrigation districts (IDs) in the Río Bravo basin, to the north of Mexico.

Table 1 shows the general data of the IDs studied. This information was extracted from the agricultural and hydrometric statistics compiled and published annually by CONAGUA (2017a). The supply main source is surface water; only IDs 005 and 009 report extractions from groundwater sources.

Table 1
General data of the agricultural year 2015-2016 of 11 irrigation districts in the Río Bravo basin, Mexico.

Sf = physical irrigable area (ha); Sr = irrigated area (ha); Vbs = gross distributed volume of surface water (hm3); Vbss = gross distributed volume of groundwater (hm3); Vb = sum of the gross distributed volumes (hm3) at the supply source level (Vb = Vbs + Vbss).

The estimation of IDs performance was obtained using the seven indicators shown in Table 2. Those performance indicators reported by Bos et al. (2005) that can be estimated with data available from official sources were chosen to evaluate IDs.

Table 2
Estimated production performance indicators for the irrigation districts (IDs) studied.

VP = economic value of total agricultural production of the IDs at current prices ($); Prod = total production (t); Sr = irrigated area (ha); Vb = sum of gross volumes extracted at source level (m3); Vn = net volume of water delivered to users at farm intake level (m3).

The rural average price (RAP) refers to the price paid to the producer for the first-hand sale of his farm, land or production area, and does not include the economic incentive granted by the federal and state government, nor the costs of transportation and sorting when the farmer brings his product to the sales center. In other words, RAP is the current price at the time the producer makes the first sale at the plot or farm.

To estimate the indicators, agricultural and hydrometric data were obtained for 15 years (2001-2002 to 2015-2016), from the agricultural statistics of the IDs reported by the CONAGUA for Vb, Sr, Vn, VP and Prod, and the financial statements of the IDs from 2012 to 2014 were used (CONAGUA, 2017b). Geospatial information on soil degradation was accessed by superimposing ID and degradation maps. This was carried out with the help of the ArcGIS v10.3 program and the data available in the Sistema Nacional de Información del Agua (SINA) of CONAGUA (2017c).

For the presentation of results, "Box-Plot", also known as box-bigot diagrams were made, used to visualize the distribution of a set of data: minimum and maximum values, quartiles (Q1, Q2 or median and Q3), existence of outliers and symmetry of the distribution. To do this, it is necessary to find the median and then the two remaining quartiles. The characteristics of this type of graph are:

  1. - The symbol * is the average of the data.

  2. - The horizontal line across the box is the median (Q2).

  3. - The lower side of the rectangle represents the first quartile (Q1, median of the lower half of the data or 25 % of the data), and the upper side represents the third quartile (Q3, median of the upper half of the data or 75 % of the data). Therefore, the height of the box represents the interquartile range (the difference between Q3 and Q1).

  4. - Vertical lines (whiskers or axes) protruding from the box extend to the minimum and maximum of the data set, as long as these values do not differ from the average by more than 1.5 times the interquartile range. The ends of the whiskers are marked by two short horizontal lines.

  5. - The values, indicated by +, below and above the whiskers, lower and upper, are considered outliers.

Graphs showing the variation of the indicators in each ID studied were created. The districts were separated into two large groups, and in order to identify them in the graphs, a symbol was assigned to each ID according to Table 3.

Table 3
Symbology used for the irrigation districts (IDs) of the Río Bravo basin, Mexico.

Results and discussion
Performance indicators

The values of the first performance indicator (RAP; $·t-1) of the 11 IDs are shown in Table 4. Due to a crop pattern concentrated in forages, the ID 006 has the lowest average RAP.

Table 4
Rural average price ($·t-1), nationwide and for 11 irrigation districts in the Río Bravo basin, Mexico.

Figure 2 shows the RAP per crop year for each ID, and the national average value is reported as a reference. A problem when valuing agricultural production at current prices is the effects on the fluctuations in the RAP of production volumes, so it is recommended to carry out an analysis at constant prices to remove these effects and homogenize the values of each year with respect to the base year (Kennedy, 2016).


Figure 2
Rural average price per year of 11 irrigation districts (IDs) in the Río Bravo basin and nationwide, Mexico

Table 5 shows the results of the descriptive statistics and the results associated with the RAP of the IDs studied. The statistics obtained are the basis of Figure 3. This graph shows high variability in the average of the RAP, and a greater variability in the IDs 025, 026 and 031, due to their crop pattern.

Table 5
Descriptive statistics of the rural average price ($·t-1) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 3
Graphical representation of descriptive statistics of the rural average price of 11 irrigation districts in the Río Bravo basin, Mexico.

The second production indicator studied was the economic productivity of land (EPL; thousands of $·ha-1). Table 6 shows the EPL results for the 11 IDs analyzed and the nationwide value. Gaps can be observed because data from some IDs were not available.

Table 6
Economic land productivity value (thousands of $·ha-1) of 11 irrigation districts in the Río Bravo basin and nationwide, Mexico.

Figure 4 shows the EPL per agricultural year of the ID in the Río Bravo basin and the nationwide value reported in Table 7.


Figure 4
Economic land productivity of 11 irrigation districts (IDs) in the Río Bravo basin and the nationwide value, Mexico.

Table 7
Descriptive statistics of land economic productivity (thousands of $ ·ha-1) of 11 irrigation districts in the Río Bravo basin, Mexico.

Table 7 shows the results of the descriptive statistics of the EPL of ID in the Río Bravo basin. These statistics are the basis of Figure 5, where the ID 050 had the greatest dispersion.


Figure 5
Graphical representation of descriptive statistics of the economic productivity of land in 11 irrigation districts in the Río Bravo basin, Mexico.

The third production indicator analyzed was yield (t·ha-1). Table 8 shows the values of this indicator for the 11 IDs and the nationwide value. It is worth mentioning that the agricultural year from 2005-2006 was very dry for several studied; therefore, IDs 004, 005, 006 and 009 did not establish irrigated area (Table 6).

Table 8
Yield (t·ha-1) obtained for 11 irrigation districts in the Río Bravo basin and the nationwide value, Mexico.

Figure 6 represents the yield per agricultural year of the ID in the Río Bravo basin and the nationwide value reported in Table 8.


Figure 6
Yield of 11 irrigation districts (IDs) in the Río Bravo basin and nationwide, Mexico.

Table 9 shows the results of the descriptive statistical measurements of the yield of the ID in the Río Bravo basin. These measurements are the basis of Figure 7.

Table 9
Descriptive yield measurements (t·ha-1) of 11 irrigation districts in the Río Bravo basin, Mexico.

The values obtained from the yield were very variable in IDs 005, 050, 090 and 103, this due to the mixture of forage crops and grains. This indicates that the interdistrict comparison of yield, as a single value for each agricultural year (Tables 8 and 9), is complicated by the fact that there is inter- and interdistrict variation in crop patterns and seasons, because it generates an overestimation of the production of perennial forage and horticultural crops over grains. This is due to the fact that different production organs, which have different humidity, are compared in relation to the yield, that is, green matter against dry matter.


Figure 7
Graphical representation of descriptive statistical yield measurements of 11 irrigation districts in the Río Bravo basin, Mexico.

The fourth production indicator studied is the economic productivity of water at source (EPWf; $·m-3). Table 10 shows the results of this indicator for the 11 IDs and nationwide.

Table 10
Economic productivity of water at level of the supply source ($·m-3) of 11 irrigation districts in the Río Bravo basin and nationwide, Mexico.

Figure 8 shows the EPWf per agricultural year of the ID in the Río Bravo basin and nationwide reported in Table 10.


Figure 8
Economic productivity of water at the level supply source for 11 irrigation districts (IDs) in the Rio Bravo basin and nationwide, Mexico

Table 11 shows the results of the descriptive statistics of EPWf of ID of the Rio Bravo Basin. These statistics are the basis of Figure 9, where ID 050 has the greatest variability.

Table 11
Descriptive statistics of the economic productivity of water at level of the supply source ($·m-3) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 9
Graphical representation of descriptive statistics of economic water productivity at level of the supply source for 11 irrigation districts in the Río Bravo basin, Mexico.

The fifth production indicator studied was water productivity at the source of supply level (WPf; kg·m-3). Table 12 shows the results obtained for this indicator for the 11 IDs and nationwide.

Table 12
Water productivity at the level of the supply source (kg·m-3) of 11 irrigation districts in the Río Bravo basin and nationwide, Mexico.

Figure 10 shows the WPf per agricultural year of the ID in the Río Bravo basin and nationwide reported in Table 12. Most of the values obtained are below the baseline of 1.62 kg·m-3 established for 2012 in the “National Development Plan 2013-2018” (CONAGUA, 2014), and the target for 2018 that was established at 1.87 kg·m-3; only five IDs had higher values in 2016.


Figure 10
Water productivity at level of the supply source of 11 irrigation districts (IDs) in the Río Bravo basin and nationwide, Mexico.

Table 13 shows the results of the descriptive statistics of the WPf of the ID of the Rio Bravo basin. These values are the basis of Figure 11, where DR 050 is the one with the greatest variability in values.

Table 13
Descriptive statistics of water productivity at level of supply source (kg·m-3) of 11 irrigation districts in the Rio Bravo basin, Mexico.


Figure 11
Graphical representation of descriptive statistics of water productivity at level of the supply source for 11 irrigation districts in the Rio Bravo basin, Mexico.

The sixth production indicator evaluated was the economic productivity of water at the user level (EPWu; $·m-3). Table 14 shows the results of that indicator for 11 IDs of the agricultural years with data availability.

Table 14
Water economic productivity at user level ($·m-3) of 11 irrigation districts of the Rio Bravo basin, Mexico.

Table 15 shows the results of the descriptive statistics of the EPWu for the ID in the Río Bravo basin. These values are the basis of Figure 12, where the high variability in water availability of ID 050 can be seen, which may be due to the cultivation pattern based on forage and fruit trees. Olmedo et al. (2017) report average EPWu values in the range of 2.8 to 6 $·m-3 for the ID 041, which are very similar to those estimated in this study, where the main crop is wheat grain.

Table 15
Descriptive statistics of economic water productivity at the user level ($·m-3) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 12
Graphical representation of descriptive statistics of economic water productivity at the user level for 11 irrigation districts in the Río Bravo basin, Mexico.

The last production indicator studied was water productivity at user level (WPu; kg·m-3). Table 16 shows the results of this indicator for the 11 IDs of the agricultural years with data availability.

Table 16
Water productivity at user level (kg·m-3) of 11 irrigation districts of the Rio Bravo basin, Mexico.

Table 17 shows the results of the descriptive statistics of the WPu of 11 ID in the Río Bravo Basin. These statistics are the basis of Figure 13, where IDs 005, 006, 025, 026, 050 and 103 show between medium and high variability; this is due to the uncertainty in the volumes delivered at the user level due to the lack of reliable estimates, as reported by Alexander (2002) for ID 041 in Mexico. Another factor may be the year-to-year change in cropping plans due to the variability in annual availability at the source level, as is the case of IDs 025 and 026.

Table 17
Descriptive statistics for water productivity at the user level (kg·m-3) of 11 irrigation districts in the Río Bravo basin, Mexico


Figure 13
Graphical representation of descriptive statistical measurements of water productivity at the user level for 11 irrigation districts in the Río Bravo basin, Mexico.

If EPL (thousands $·ha-1) and yield (t·ha-1) are related, then RAP (Equation 1) is obtained.

R A P = E P L Y i e l d = V P S r P r o d S r = V P P r o d = ( $ ) ( t ) (1)

With regard to total production (Prod), if we consider RAP, yield, WPf and WPu, we can see that as production increases, the values of the indicators increase. Table 18 shows the average values of each production performance indicator per ID.

Table 18
Average values of the seven indicators evaluated per irrigation district in the Río Bravo basin and nationwide, Mexico.

The estimated values of the seven performance indicators are within the range reported by Altamirano-Aguilar et al. Table 19 shows an analysis of the indicators with respect to their average, highlighting the districts with the highest and lowest values. IDs 031, 050 and 113 show the values with the highest dispersion with respect to the average of the basin ID. The data reported in this table indicate that it is not feasible to use a single indicator to evaluate performance, but several complementary indicators are required to characterize ID integrally, this is due to the complexity of the agronomic, environmental, political and socio-economic factors defining water and land productivity of ID.

Table 19
Average values of the distribution of seven performance indicators of 11 irrigation districts (ID) in the Río Bravo basin, Mexico (from 2002 to 2016)

The data in brackets indicates the irrigation district with the highest or lowest average value. The reference column is based on the study of Altamirano-Aguilar et al. (2017).

Indicators regarding the value of production (VP) at current prices, as is the case of RAP, show a positive trend (Figure 14) due to the effect of the increase in production costs and inflation.


Figure 14
Rural average price of three irrigation districts (IDs) in the Río Bravo basin, Mexico.

Since there is great variation between indicator values at the ID level, a more detailed analysis at the irrigation module level is recommended. This is because each irrigation module is autonomous, and they are responsible for delivering the irrigation service to the users and conserving the hydro-agricultural infrastructure under concession.

Table 20 shows a dispersion analysis of the production per unit of water extracted from the supply source of the 11 IDs.

Table 20
Analysis of water productivity dispersion at level of the supply source (WPf) per irrigation district (IDs) analyzed.

By studying the correlation of two production performance indicators, it is possible to determine the conduction efficiency (CE) of the supply source to the farm intake, where it is delivered to the user. In this case, the related indicators are WPf and WPu, as shown in the following equation:

C E = W P f W P u = ( P r o d / V b ) ( P r o d / V n ) = V b V n = m 3 m 3 (2)

Table 21 shows the conduction efficiencies obtained from Equation 2 of the 11 IDs studied, and Figure 15 shows the efficiencies of IDs 004 and 005, where ID 050 stands out. It is worth mentioning that most Mexican IDs were designed with a conduction efficiency of 70%, assuming earth-lined channels (SRH, 1973).

Table 21
Conduction efficiencies of 11 irrigation districts in the Rio Bravo basin, Mexico

In general, conduction efficiencies remained almost constant over the five years studied. Based on the results obtained (Table 21 and Figure 15), it can be deduced that the large investments made to improve the conduction network of many IDs have not translated into a significant increase in conduction efficiency, from the source of supply to the farm. This was possibly coupled with limited conservation of the IDs studied.


Figure 15
Conduction efficiency of three irrigation districts (IDs) in the Río Bravo basin, Mexico.

Conclusions

The most common indicators for evaluating the performance of an ID in Mexico are yield and global conduction efficiency. However, as the results indicate, no single performance indicator can be used, but several complementary indicators are required to characterize IDs, integrally. Inter-district comparison of indicator values is complicated due to district variation in cropping cycles and patterns, resulting in an overestimation of the production of perennial forage and horticultural crops over grains.

The values of conduction efficiency of hydraulic infrastructure of IDs are below those contemplated in the original design of IDs. This indicates a degradation of the irrigation infrastructure, possibly due to limited conservation or operation of the IDs studied.

The productive performance of IDs is low due to a series of structural and non-structural factors that limit development at the irrigation area level. Some of the factors are low efficiency of conduction network (from the supply source to the farm), high inter-annual variability of available volumes at the source level, low irrigation fee, low technological level and increase in production costs, among others.

It is recommended to carry out the performance analysis per irrigation module and, to be not only productive, but also operational and administrative. This is the responsibility of the ACUs, because they are responsible for delivering the irrigation service to the users and for conserving the hydro-agricultural infrastructure under concession.

To dispose of unused water, one way is to improve planning, distribution and conservation of the distribution network. In addition, it is necessary to conduct a more detailed analysis of the irrigation service offered by the ACUs based on performance indicators at the ACU level, and not integrally as shown in this study.

The indicators used and results obtained can be used to evaluate the production behavior of IDs, as well as to analyze the investment policies to improve the hydro-agricultural infrastructure (both of the distribution network and of the farm technification), and agricultural policies of subsidies through guarantee prices and support to the agricultural areas under irrigation. This should be reflected in a change in performance indicators, since the value of irrigation water should be maximized for the benefit of producers and society.

Supplementary material
References
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Kennedy, D. (2016). Fundamentos económicos y cuentas nacionales: una propuesta de medición de la evolución del valor. Cuadernos de Economía, 35(68), 407-431. doi: 10.15446/cuad.econ.v35n68.41662
Malano, H., Burton, M., & Makin, I. (2004). Benchmarking performance in the irrigation and drainage sector: a tool for change. Irrigation and Drainage , 53(2), 119-133. doi: 10.1002/ird.126
Olmedo-Vázquez, V. M., Camacho-Poyato, E., Rodríguez-Díaz, J. A., Minjares-Lugo, J. L., & Hernández-Hernández, M. L. (2017). Determinación de indicadores de gestión en los módulos del distrito de riego núm. 041, Río Yaqui (Sonora, México). Revista de la Facultad de Ciencias Agrarias, 49(2), 149-168. Retrieved from https://core.ac.uk/download/pdf/143469076.pdf
Palacios-Vélez, E. (2000). Benefits and second generation problems of irrigation management transfer in Mexico. In: Svendsen, M., & Groenfeldt, D. (Eds), Participatory irrigation management case studies series. Washington D. C.: World Bank and the International Irrigation Management Institute.
Ruiz-Carmona, V. M., Ojeda-Bustamante, W., & Contijoch, M. (2006). Evaluación rápida de una zona de riego típica de Pakistán. Ingeniería Hidráulica en México, 21(3), 43-56. Retrieved from http://www.revistatyca.org.mx/ojs/index.php/tyca/article/download/1079/968
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Notes
Author notes

*Corresponding author: mic@tlaloc.imta.mx, tel. 777 329 3600.


Figure 1
Location of the irrigation districts (IDs) in the Río Bravo basin, to the north of Mexico.
Table 1
General data of the agricultural year 2015-2016 of 11 irrigation districts in the Río Bravo basin, Mexico.

Sf = physical irrigable area (ha); Sr = irrigated area (ha); Vbs = gross distributed volume of surface water (hm3); Vbss = gross distributed volume of groundwater (hm3); Vb = sum of the gross distributed volumes (hm3) at the supply source level (Vb = Vbs + Vbss).
Table 2
Estimated production performance indicators for the irrigation districts (IDs) studied.

VP = economic value of total agricultural production of the IDs at current prices ($); Prod = total production (t); Sr = irrigated area (ha); Vb = sum of gross volumes extracted at source level (m3); Vn = net volume of water delivered to users at farm intake level (m3).
Table 3
Symbology used for the irrigation districts (IDs) of the Río Bravo basin, Mexico.

Table 4
Rural average price ($·t-1), nationwide and for 11 irrigation districts in the Río Bravo basin, Mexico.

Figure 2 shows the RAP per crop year for each ID, and the national average value is reported as a reference. A problem when valuing agricultural production at current prices is the effects on the fluctuations in the RAP of production volumes, so it is recommended to carry out an analysis at constant prices to remove these effects and homogenize the values of each year with respect to the base year (Kennedy, 2016).

Figure 2
Rural average price per year of 11 irrigation districts (IDs) in the Río Bravo basin and nationwide, Mexico
Table 5
Descriptive statistics of the rural average price ($·t-1) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 3
Graphical representation of descriptive statistics of the rural average price of 11 irrigation districts in the Río Bravo basin, Mexico.
Table 6
Economic land productivity value (thousands of $·ha-1) of 11 irrigation districts in the Río Bravo basin and nationwide, Mexico.


Figure 4
Economic land productivity of 11 irrigation districts (IDs) in the Río Bravo basin and the nationwide value, Mexico.
Table 7
Descriptive statistics of land economic productivity (thousands of $ ·ha-1) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 5
Graphical representation of descriptive statistics of the economic productivity of land in 11 irrigation districts in the Río Bravo basin, Mexico.
Table 8
Yield (t·ha-1) obtained for 11 irrigation districts in the Río Bravo basin and the nationwide value, Mexico.


Figure 6
Yield of 11 irrigation districts (IDs) in the Río Bravo basin and nationwide, Mexico.
Table 9
Descriptive yield measurements (t·ha-1) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 7
Graphical representation of descriptive statistical yield measurements of 11 irrigation districts in the Río Bravo basin, Mexico.
Table 10
Economic productivity of water at level of the supply source ($·m-3) of 11 irrigation districts in the Río Bravo basin and nationwide, Mexico.


Figure 8
Economic productivity of water at the level supply source for 11 irrigation districts (IDs) in the Rio Bravo basin and nationwide, Mexico
Table 11
Descriptive statistics of the economic productivity of water at level of the supply source ($·m-3) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 9
Graphical representation of descriptive statistics of economic water productivity at level of the supply source for 11 irrigation districts in the Río Bravo basin, Mexico.
Table 12
Water productivity at the level of the supply source (kg·m-3) of 11 irrigation districts in the Río Bravo basin and nationwide, Mexico.


Figure 10
Water productivity at level of the supply source of 11 irrigation districts (IDs) in the Río Bravo basin and nationwide, Mexico.
Table 13
Descriptive statistics of water productivity at level of supply source (kg·m-3) of 11 irrigation districts in the Rio Bravo basin, Mexico.


Figure 11
Graphical representation of descriptive statistics of water productivity at level of the supply source for 11 irrigation districts in the Rio Bravo basin, Mexico.
Table 14
Water economic productivity at user level ($·m-3) of 11 irrigation districts of the Rio Bravo basin, Mexico.

Table 15
Descriptive statistics of economic water productivity at the user level ($·m-3) of 11 irrigation districts in the Río Bravo basin, Mexico.


Figure 12
Graphical representation of descriptive statistics of economic water productivity at the user level for 11 irrigation districts in the Río Bravo basin, Mexico.
Table 16
Water productivity at user level (kg·m-3) of 11 irrigation districts of the Rio Bravo basin, Mexico.

Table 17
Descriptive statistics for water productivity at the user level (kg·m-3) of 11 irrigation districts in the Río Bravo basin, Mexico


Figure 13
Graphical representation of descriptive statistical measurements of water productivity at the user level for 11 irrigation districts in the Río Bravo basin, Mexico.
Table 18
Average values of the seven indicators evaluated per irrigation district in the Río Bravo basin and nationwide, Mexico.

Table 19
Average values of the distribution of seven performance indicators of 11 irrigation districts (ID) in the Río Bravo basin, Mexico (from 2002 to 2016)

The data in brackets indicates the irrigation district with the highest or lowest average value. The reference column is based on the study of Altamirano-Aguilar et al. (2017).

Figure 14
Rural average price of three irrigation districts (IDs) in the Río Bravo basin, Mexico.
Table 20
Analysis of water productivity dispersion at level of the supply source (WPf) per irrigation district (IDs) analyzed.

Table 21
Conduction efficiencies of 11 irrigation districts in the Rio Bravo basin, Mexico


Figure 15
Conduction efficiency of three irrigation districts (IDs) in the Río Bravo basin, Mexico.
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