Recent from talks
Nothing was collected or created yet.
Water-use efficiency
View on WikipediaWater-use efficiency (WUE) refers to the ratio of plant biomass to water lost by transpiration, can be defined either at the leaf, at the whole plant or a population/stand/field level:
- leaf level : photosynthetic water-use efficiency (also called instantaneous water-use efficiency WUEinst), which is defined as the ratio of the rate of net CO2 carbon assimilation (photosynthesis) to the rate of transpiration or stomatal conductance,[1] then called intrinsic water-use efficiency[2] (iWUE or Wi)
- plant level : water-use efficiency of productivity (also called integrated water-use efficiency or transpiration efficiency,TE), which is typically defined as the ratio of dry biomass produced to the rate of transpiration.[3]
- field level : based on measurements of CO2 and water fluxes over a field of a crop or a forest, using the eddy covariance technique[4]
Research to improve the water-use efficiency of crop plants has been ongoing from the early 20th century, however with difficulties to actually achieve crops with increased water-use efficiency.[5]
Intrinsic water-use efficiency Wi usually increases during soil drought, due to stomatal closure and a reduction in transpiration, and is therefore often linked to drought tolerance. Observations from several authors[3][6][7][8] have however suggested that WUE would rather be linked to different drought response strategies, where
- low WUE plants could either correspond to a drought tolerance strategy, for example by anatomical adaptations reducing vulnerability to xylem cavitation, or to a drought avoidance/water spender strategy through a wide soil exploration by roots or a drought escape strategy due to early flowering
- whereas high WUE plants could correspond to a drought avoidance/water saving strategy, through drought-sensitive, early closing stomata.
Increases in water-use efficiency are commonly cited as a response mechanism of plants to moderate to severe soil water deficits and have been the focus of many programs that seek to increase crop tolerance to drought.[9] However, there is some question as to the benefit of increased water-use efficiency of plants in agricultural systems, as the processes of increased yield production and decreased water loss due to transpiration (that is, the main driver of increases in water-use efficiency) are fundamentally opposed.[10][11] If there existed a situation where water deficit induced lower transpirational rates without simultaneously decreasing photosynthetic rates and biomass production, then water-use efficiency would be both greatly improved and the desired trait in crop production.
Water-use efficiency is also a much studied trait in Plant ecology, where it has been used already in the early 20th century to study the ecological requirements of Herbaceous plants[12] or forest trees,[13] and is still used today, for example related to a drought-induced limitation of tree growth[14]
References
[edit]- ^ Farquhar, G.D.; Rashke, K. (1978). "On the resistance to transpiration of the sites of evaporation within the leaf". Plant Physiology. 61 (6): 1000–1005. doi:10.1104/pp.61.6.1000. PMC 1092028. PMID 16660404.
- ^ Meinzer, F. C., Ingamells, J. L., Crisosto, C. (1991). "Carbon Isotope Discrimination correlates with bean yield of diverse coffee seedling populations". HortScience. 26 (11): 1413–1414. doi:10.21273/HORTSCI.26.11.1413.
- ^ a b Maximov, N. A. (1929). The plant in relation to water. George Allen & Unwin LTD London.
- ^ Tallec, T.; Béziat, P.; Jarosz, N.; Rivalland, V.; Ceschia, E. (2013). "Crops' water use efficiencies in temperate climate: Comparison of stand, ecosystem and agronomical approaches". Agricultural and Forest Meteorology. 168: 69–81. Bibcode:2013AgFM..168...69T. doi:10.1016/j.agrformet.2012.07.008.
- ^ Vadez, V.; Kholova, J.; Medina, S.; Kakkera, A.; Anderberg, H. (2014). "Transpiration efficiency: new insights into an old story". Journal of Experimental Botany. 65 (21): 6141–6153. doi:10.1093/jxb/eru040. PMID 24600020.
- ^ Ehleringer, J. R. (1993). "Variation in Leaf Carbon-Isotope Discrimination in Encelia farinosa : Implications for Growth Competition and Drought Survival". Oecologia. 95 (3): 340–346. Bibcode:1993Oecol..95..340E. doi:10.1007/BF00320986. ISSN 0029-8549. PMID 28314008.
- ^ Kenney, A. M., McKay, J. K., Richards, J. H., Juenger, T. E. (2014). "Direct and indirect selection on flowering time, water-use efficiency (WUE, δ13C), and WUE plasticity to drought in Arabidopsis thaliana". Ecology and Evolution. 4 (23): 4505–4521. Bibcode:2014EcoEv...4.4505K. doi:10.1002/ece3.1270. ISSN 2045-7758. PMC 4264900. PMID 25512847.
- ^ Campitelli, B. E., Des Marais, D. L., Juenger, T. E. (February 2016). "Ecological interactions and the fitness effect of water-use efficiency: Competition and drought alter the impact of natural MPK12 alleles in Arabidopsis". Ecology Letters. 19 (4): 424–434. Bibcode:2016EcolL..19..424C. doi:10.1111/ele.12575. ISSN 1461-023X. PMID 26868103.
- ^ Condon, A. G., Richards, R. A., Rebetzke, G. J., Farquhar, G. D. (2004). "Breeding for high water-use efficiency". Journal of Experimental Botany. 55 (407): 2447–2460. doi:10.1093/jxb/erh277. ISSN 0022-0957. PMID 15475373.
- ^ Bacon, M. Water Use Efficiency in Plant Biology. Oxford: Blackwell Publishing Ltd., 2004. ISBN 1-4051-1434-7. Print.
- ^ Blum, A. (2009). "Effective use of water (EUW) and not water-use efficiency (WUE) is the target of crop yield improvement under drought stress". Field Crops Research. 112 (2–3): 119–123. Bibcode:2009FCrRe.112..119B. doi:10.1016/j.fcr.2009.03.009.
- ^ Iljin, V. (1916). "Relation of transpiration to assimilation in steppe plants". Journal of Ecology. 4 (2): 65–82. Bibcode:1916JEcol...4...65I. doi:10.2307/2255326. JSTOR 2255326.
- ^ Bates, C.G. (1923). "Physiological requirements of Rocky Mountain trees". Journal of Agricultural Research. 24: 97–164.[1]
- ^ Linares, J. C.; Camarero, J.J. (2012). "From pattern to process: linking intrinsic water-use efficiency to drought-induced forest decline". Global Change Biology. 18 (3): 1000–1015. Bibcode:2012GCBio..18.1000L. doi:10.1111/j.1365-2486.2011.02566.x.
Further reading
[edit]- Vadez, V., Kholova, J., Medina, S., Kakkera, A., Anderberg, H. (2014). "Transpiration efficiency: New insights into an old story". Journal of Experimental Botany. 65 (21): 6141–6153. doi:10.1093/jxb/eru040. ISSN 1460-2431. PMID 24600020.
- Lambers, H.; Chapin, F. S.; Pons, T. L. (2008). Plant Physiological Ecology. New York: Springer. ISBN 9780387783413.
- Tambussi, E. A.; Bort, J.; Araus, J. L. (2007). "Water use efficiency in C3 cereals under Mediterranean conditions: a review of physiological aspects". Annals of Applied Biology. 150 (3): 307–321. doi:10.1111/j.1744-7348.2007.00143.x.
- Condon, A. G., Richards, R. A., Rebetzke, G. J., Farquhar, G. D. (2004). "Breeding for high water-use efficiency". Journal of Experimental Botany. 55 (407): 2447–2460. doi:10.1093/jxb/erh277. ISSN 0022-0957. PMID 15475373.
- Cregg, B. M. (2004). "Improving Drought Tolerance of Trees: Theoretical and practical considerations". Acta Horticulturae. 630 (630): 147–158. doi:10.17660/ActaHortic.2004.630.18. ISSN 0567-7572.
Water-use efficiency
View on GrokipediaDefinition and Concepts
Basic Definition
Water-use efficiency (WUE) is a fundamental concept in plant physiology, defined as the ratio of carbon assimilated—typically measured as biomass production or grain yield—per unit of water consumed by plants or crops. This metric quantifies how effectively plants convert water into productive output, reflecting the inherent trade-off between carbon fixation through photosynthesis and water loss primarily via transpiration.[1] Common units for WUE include kilograms of dry biomass per cubic meter of water (kg/m³) for crop-level assessments or grams of biomass per kilogram of water transpired (g/kg) for physiological evaluations.[6] The concept of WUE originated in early 20th-century plant physiology research, where it was first formalized by Lyman J. Briggs and Homer L. Shantz in their 1913 USDA bulletin The Water Requirement of Plants.[7] In this seminal work, they experimentally determined the water requirements of various species grown in controlled conditions, establishing WUE as the dry matter produced divided by the water transpired, based on field trials in the Great Plains.[7] Their findings highlighted species-specific variations, laying the groundwork for understanding water conservation in arid environments and influencing subsequent agricultural practices.[8] WUE can be distinguished at different scales: intrinsic WUE refers to the instantaneous leaf-level ratio of net photosynthetic rate (A, in μmol CO₂ m⁻² s⁻¹) to stomatal conductance (gₛ, in mol H₂O m⁻² s⁻¹), capturing real-time gas exchange dynamics under varying environmental conditions.[9] In contrast, integrated WUE encompasses the cumulative carbon assimilation relative to total water use over longer growth periods, such as a full cropping cycle, integrating factors like soil evaporation and whole-plant transpiration.[1] For instance, in agricultural contexts, integrated WUE is commonly expressed as crop yield (e.g., kg/ha) divided by seasonal water use (e.g., transpiration plus evaporation in mm or m³), providing a practical measure for yield optimization.[10]Types of Water-use Efficiency
Water-use efficiency (WUE) encompasses several distinct types, differentiated primarily by the scale of measurement and the context of application, ranging from physiological processes in individual plants to broader economic considerations in resource management.[1] Instantaneous WUE refers to the ratio of net photosynthesis to transpiration at the leaf level, capturing short-term physiological responses to environmental conditions and proving valuable for studies on gas exchange dynamics.[1] This type emphasizes momentary carbon assimilation relative to water loss through stomata, often varying with factors like light intensity and vapor pressure deficit.[1] Integrated or seasonal WUE measures biomass accumulation or crop yield per unit of total water consumed over an entire growing period, serving as a key metric in agricultural evaluations of long-term resource utilization.[1] It integrates water inputs from precipitation, irrigation, and soil storage to assess overall productivity, commonly applied to field crops like maize and wheat to gauge varietal improvements.[1] Ecosystem-level WUE quantifies net primary productivity or gross primary productivity per unit of evapotranspiration across natural or managed landscapes, reflecting the balance of carbon and water cycles at larger scales.[1] In arid regions, this type typically ranges from 0.5 to 2 g C/kg H₂O, influenced by vegetation composition such as shrubs or grasses that adapt to water scarcity.[11] Economic WUE extends the concept to incorporate financial outcomes, defined as the value added in a sector—such as agricultural yield value—per unit volume of water used, including irrigation costs to evaluate cost-effectiveness in water-scarce areas.[12] This approach is particularly relevant for irrigated agriculture, where it accounts for gross value added from crops excluding rainfed components, aiding policy decisions on water allocation.[12]Measurement and Calculation
Field-scale Methods
Field-scale methods for measuring water-use efficiency (WUE) focus on integrating water inputs and outputs over entire crop plots or fields to quantify overall crop performance, typically expressed as seasonal integrated WUE. These approaches rely on agronomic measurements of water fluxes and yield, providing practical insights for irrigation management without delving into plant-level processes. The water balance method estimates evapotranspiration (ET) by accounting for all water components in a defined field area, calculated as precipitation plus irrigation inputs minus the change in soil moisture storage minus runoff and drainage.[13] This technique allows for direct computation of crop water use, enabling WUE assessment through the ratio of biomass or yield to total ET. It is particularly useful for evaluating irrigation efficiency in field trials, where boundary conditions like runoff collection are monitored to close the balance accurately. Yield-based calculations determine WUE as the ratio of harvestable yield to seasonal ET, often employing weighing lysimeters for precise quantification of water fluxes. Weighing lysimeters consist of soil monoliths containing crops, mounted on scales to measure mass changes attributable to ET, with accuracy typically within 5% for field-scale WUE estimates. Invented in the 19th century, these devices have become a standard for developing crop coefficients and validating irrigation schedules by capturing daily to seasonal water use dynamics. The general equation for crop WUE at the field scale is: For wheat, representative values range from 10 to 20 kg/ha/mm, reflecting variations in management and environment under optimal conditions. Remote sensing approaches estimate field-scale WUE by combining satellite-derived vegetation indices, such as the Normalized Difference Vegetation Index (NDVI), with models like the Surface Energy Balance Algorithm for Land (SEBAL) to derive biomass production and ET. NDVI assesses crop canopy development to proxy biomass, while SEBAL partitions surface energy fluxes for ET estimation, achieving accuracies of 85% on a daily basis and up to 95% seasonally at the field scale. This method facilitates large-area monitoring, supporting scalable WUE assessments in irrigated agriculture.Physiological Methods
Physiological methods for assessing water-use efficiency (WUE) at the leaf and plant level primarily involve direct measurements of photosynthetic gas exchange and indirect proxies such as stable isotopes and chlorophyll fluorescence, enabling insights into cellular and stomatal mechanisms under controlled conditions. These techniques focus on the ratio of carbon assimilation to water loss, providing mechanistic understanding without relying on whole-plant or field-scale integrations. Gas exchange analysis quantifies intrinsic WUE, defined as the ratio of net photosynthesis rate (A, in μmol CO₂ m⁻² s⁻¹) to stomatal conductance (g_s, in mmol H₂O m⁻² s⁻¹), yielding units of μmol CO₂ per mmol H₂O. This instantaneous measure, often denoted as A/g_s, reflects the efficiency of CO₂ uptake relative to transpiration at the leaf level and is commonly assessed using portable systems like the LI-6400 or LI-6800 infrared gas analyzers (IRGAs), which simultaneously monitor CO₂ and H₂O fluxes in a controlled leaf chamber. Handheld porometers, such as the AP4 or SC-1, offer a complementary, rapid assessment of g_s by measuring diffusive resistance to water vapor through stomata, facilitating high-throughput leaf-level evaluations. In C₃ plants under ambient CO₂ concentrations (around 400 μmol mol⁻¹), intrinsic WUE typically ranges from 50 to 100 μmol mol⁻¹, varying with environmental cues like vapor pressure deficit. Stable isotope analysis serves as a non-destructive proxy for long-term intrinsic WUE by examining carbon isotope discrimination (Δ¹³C) in leaf tissue, which inversely correlates with A/g_s. The relationship is approximated by the equation Δ¹³C ≈ a + (b - a) (c_i/c_a), where a (≈4.4‰) is the fractionation during CO₂ diffusion, b (≈27‰) is the net fractionation during carboxylation in C₃ plants, and c_i/c_a is the ratio of intercellular to ambient CO₂ concentration; higher WUE corresponds to lower Δ¹³C and thus less negative δ¹³C values (typically -28‰ to -22‰ in C₃ leaves). Developed in the 1980s, this method enables efficient screening of plant genotypes for inherent WUE traits by analyzing bulk leaf or seed carbon isotopes via mass spectrometry, avoiding the need for repeated gas exchange measurements over time. Chlorophyll fluorescence provides an indirect evaluation of WUE under water stress by monitoring photosystem II (PSII) efficiency, as drought-induced stomatal closure limits CO₂ availability, reducing photochemical quenching and increasing non-photochemical dissipation. Key parameters include the maximum quantum efficiency of PSII (F_v/F_m, typically 0.75–0.85 in unstressed leaves) and the effective quantum yield (Φ_PSII), which decline under water deficit, signaling impaired photosynthetic performance and associated WUE trade-offs. This optical technique, using pulse-amplitude modulated (PAM) fluorometers, allows real-time, non-invasive assessment of stress impacts on electron transport without direct gas measurements.Factors Affecting Water-use Efficiency
Environmental Factors
Environmental factors play a critical role in influencing water-use efficiency (WUE) in plants, primarily through their effects on transpiration and photosynthesis rates. Temperature is a key driver, with optimal ranges varying by crop but generally between 15-30°C promoting balanced stomatal conductance and photosynthetic activity, thereby maximizing WUE. Extremes beyond this range, such as high temperatures above 30°C, reduce WUE by elevating the vapor pressure deficit (VPD), which accelerates transpiration without a proportional increase in carbon assimilation, leading to greater water loss relative to biomass production.[1] Atmospheric CO₂ concentration also significantly impacts WUE, as elevated levels—such as an increase of +200 ppm above ambient—can enhance it by 20-50% through partial closure of stomata, which conserves water while sustaining photosynthesis. This mechanism reduces transpiration rates, allowing plants to maintain higher intrinsic WUE under ambient to moderately elevated CO₂ conditions. Soil moisture availability and salinity further modulate WUE; drought conditions lower it by inducing stomatal closure that limits both water uptake and photosynthetic efficiency, resulting in reduced overall biomass per unit water used. Soil salinity decreases WUE in sensitive crops by impairing root water absorption and exacerbating osmotic stress, which induces partial stomatal closure and reduces yield; for example, in tomatoes, salinity levels around 1 dS/m can reduce yield by 20-30%.[14] Light intensity also affects WUE, with higher levels generally increasing carbon assimilation but potentially raising transpiration demands under high VPD. Humidity and wind interact to alter evaporative demand, with low humidity increasing transpiration rates and reduces WUE by widening the VPD gradient across leaf surfaces. Wind exacerbates this by enhancing boundary layer conductance, promoting faster water vapor diffusion from leaves and soil, which further strains plant water status without benefiting carbon gain. In regions like Mediterranean climates, seasonal rainfall variability can reduce WUE compared to more stable temperate zones due to erratic water availability that disrupts consistent transpiration control and growth.[15][16]Biological Factors
Biological factors significantly influence water-use efficiency (WUE) in plants through intrinsic physiological, genetic, and symbiotic mechanisms that optimize carbon assimilation relative to water loss. These traits enable plants to maintain productivity under varying internal constraints, primarily by enhancing resource capture and regulating gas exchange. The photosynthetic pathway is a key determinant of WUE, with C4 plants such as maize demonstrating approximately 50% higher WUE than C3 plants like rice and wheat. This advantage arises from the CO2 concentrating mechanism in C4 photosynthesis, which minimizes photorespiration and allows for reduced stomatal opening while sustaining high rates of carbon fixation.[17][18] Root architecture also plays a crucial role, particularly through the development of deep root systems that enhance water access in dry soils. Deep roots can improve WUE by 15-25% by tapping into subsurface water reserves, thereby increasing water uptake without proportionally raising transpiration.[19][20] Stomatal regulation, mediated by abscisic acid (ABA), further modulates WUE by promoting stomatal closure in response to water stress signals. This ABA-induced response conserves water by limiting transpiration, though it simultaneously restricts CO2 uptake and can constrain photosynthetic rates.[21][22] Microbial interactions, especially with mycorrhizal fungi, bolster WUE by extending the root system's absorptive capacity. Arbuscular mycorrhizal fungi can increase WUE by about 20% through improved phosphorus uptake and enhanced water absorption via their hyphal networks, which facilitate nutrient and water transport to the host plant.[23] At the genetic level, quantitative trait loci (QTLs) for WUE have been identified in crops like rice since the early 2000s, often linking to genes such as ERECTA that control stomatal density. These QTLs influence transpiration efficiency by altering stomatal characteristics, providing targets for breeding higher WUE varieties.[25][26]Importance and Applications
Agricultural Applications
In agricultural systems, water-use efficiency (WUE) is pivotal for optimizing crop yields while conserving limited water resources, particularly in irrigated and rainfed farming contexts where water scarcity affects productivity. Deficit irrigation, a key scheduling strategy, applies less water than full crop evapotranspiration needs during non-critical growth stages, thereby enhancing WUE without severely compromising yields. For instance, in tomato production, deficit irrigation strategies have been shown to enhance WUE compared to full irrigation, as it aligns water supply more closely with plant physiological demands, reducing evaporation losses and promoting deeper root systems.[27] Crop rotation combined with residue management further bolsters WUE by improving soil structure and water retention. Incorporating cereal crop residues into the soil elevates organic matter content, which enhances infiltration and reduces runoff, leading to WUE improvements of 7.5-25.5% depending on initial soil organic levels; in soils with 10-15 g/kg organic matter, gains average around 19%. This practice is especially beneficial for cereals like wheat and maize, where residue retention mitigates soil erosion and sustains moisture availability during dry spells.[28] Benchmarking WUE in major crops provides context for global agricultural performance. For maize, a staple crop, global averages range from 1.2-2.3 kg/m³ of water, reflecting variations across irrigated and rainfed systems; however, in rainfed agriculture of sub-Saharan Africa, WUE often falls below 1 kg/m³ due to erratic rainfall, poor soil fertility, and limited management, exacerbating yield gaps of up to 47% relative to potential. These benchmarks underscore the need for targeted interventions in low-efficiency regions.[29][30] Economically, enhancing WUE in water-scarce areas like India yields substantial benefits by lowering input costs and bolstering food security. Improved WUE through efficient practices can reduce overall water-related expenses by up to 20-30%, including pumping and irrigation infrastructure, while supporting higher net farm incomes—potentially increasing them by 30% in groundwater-dependent regions—and enabling sustained production for over 600 million agricultural dependents. FAO analyses from 2020 on precision farming highlight how such approaches can boost yields by 10-15% with 20-40% less water, amplifying these economic and security outcomes without delving into specific agronomic details.[31][32][33]Ecological Applications
In natural ecosystems, water-use efficiency (WUE) serves as a key indicator of drought resilience, particularly in forests and grasslands where water availability shapes ecosystem dynamics. During drought events, many forest and grassland systems exhibit increased WUE as plants reduce transpiration while maintaining or recovering carbon assimilation, demonstrating adaptive resilience. For instance, in semi-arid savannas, long-term WUE typically ranges from 1 to 3 g C per kg H₂O, reflecting efficient resource use that allows these ecosystems to persist under variable rainfall regimes.[34] This resilience is evident in post-drought recovery, where arid ecosystems show significant WUE elevation, underscoring their capacity to rebound from water stress without long-term productivity losses. Elevated atmospheric CO₂ concentrations further enhance ecosystem WUE by improving photosynthetic efficiency and stomatal control, which in turn boosts carbon sequestration. Models indicate that this CO₂ fertilization effect can increase carbon storage in forests and grasslands by 10-20% under future scenarios, as reduced water loss per unit of carbon fixed amplifies net ecosystem productivity.[35] Such improvements are particularly pronounced in semi-arid regions, where higher WUE mitigates water limitations and supports greater biomass accumulation over time. In arid biomes, species exhibiting high intrinsic WUE often dominate community structures, influencing overall biodiversity and ecosystem composition. These adaptations, such as enhanced stomatal regulation and deep root systems, allow drought-tolerant plants like shrubs and perennial grasses to outcompete others, thereby shaping vegetation patterns and maintaining ecosystem stability amid water scarcity. This selective dominance fosters biodiversity hotspots in resilient communities, where high-WUE species contribute to soil conservation and habitat provision.[36] Ecological restoration projects leverage WUE monitoring to assess success in degraded landscapes, as seen in China's Loess Plateau, where large-scale reforestation since 2000 has significantly elevated ecosystem WUE through increased vegetation cover and gross primary productivity relative to evapotranspiration.[37] Deforestation in tropical forests diminishes global carbon sinks, as it leads to carbon release and weakens the forests' role in mitigating climate change.[38]Strategies for Improvement
Agronomic Practices
Agronomic practices play a crucial role in enhancing water-use efficiency (WUE) in agricultural systems by optimizing soil moisture retention, reducing unproductive water losses, and aligning resource inputs with crop needs. These field-level techniques, including mulching, reduced tillage, and nutrient management, promote sustainable water use without relying on genetic modifications or advanced technologies. By minimizing evaporation and improving soil structure, such practices can lead to measurable gains in WUE, particularly in water-limited environments like row crop production. Mulching and cover cropping are effective strategies for conserving soil water in row crops such as maize and wheat. These methods create a physical barrier on the soil surface, significantly reducing evaporation losses and thereby increasing the proportion of water available for transpiration and crop growth. For instance, straw mulching has been shown to boost WUE by approximately 20% in both maize and wheat under varying water inputs, while plastic mulching can achieve up to 28% improvement in wheat systems at higher water inputs (>250 mm). Cover crops further enhance this by improving soil organic matter and infiltration, contributing to long-term water retention in row crop fields.[39] Reducing tillage, particularly through no-till systems, conserves soil water by preserving residue cover and minimizing soil disturbance. In wheat production, such practices have been associated with enhanced WUE due to better moisture storage and reduced runoff, with yield and efficiency gains in semi-arid regions. Similarly, optimizing fertilizer application, especially balanced nitrogen (N) rates, avoids excessive luxury uptake that diverts water to non-productive growth, potentially enhancing WUE by 10-15%. This is achieved by synchronizing N supply with crop demand, as seen in wheat where integrated water and N management improved water productivity by 15%.[40] Crop selection tailored to local conditions also elevates WUE; for example, drought-tolerant varieties like sorghum in semi-arid zones exhibit higher WUE than less adapted cereals such as wheat due to efficient root systems and reduced transpiration under stress. These practices collectively underscore the potential for agronomic management to sustain productivity amid water scarcity.Genetic and Technological Approaches
Genetic approaches to enhancing water-use efficiency (WUE) in crops have advanced through marker-assisted breeding and transgenic methods, targeting genes associated with stomatal control to optimize water loss and carbon assimilation. For instance, transgenic manipulation of genes like TaEPF1 has reduced stomatal density in wheat, leading to improved intrinsic WUE without severe yield loss. Breeding programs continue to identify traits for reduced transpiration under drought conditions.[41][42] Genome editing technologies, particularly CRISPR-Cas9, offer precise modifications to genes involved in water transport. Studies have demonstrated improvements in root hydraulic conductivity and reduced water loss in crops like rice through genetic modifications related to aquaporins, enhancing WUE under water-limited conditions.[43] Technological innovations in precision agriculture integrate sensors, IoT devices, and artificial intelligence to enable real-time irrigation management, particularly in water-intensive crops like grapes. In vineyards, AI algorithms analyze data from soil moisture sensors, weather forecasts, and plant stress indicators to automate drip irrigation, achieving water savings of 25-40% while sustaining or improving fruit quality and yield. Recent studies report broader water conservation of 30-60% in precision irrigation systems across crops.[44][45][46] Controlled environment agriculture (CEA), including hydroponic systems, represents a high-tech paradigm for maximizing WUE by recirculating nutrient solutions and eliminating soil evaporation losses. In hydroponics, water use can be as low as 10% of that required in open-field production for crops like lettuce and tomatoes, translating to 5-10 times higher WUE due to precise delivery and reuse of water. This approach is especially impactful in urban or arid settings where resource efficiency is paramount.[47][48] A notable application of these genetic advancements is the Water Efficient Maize for Africa (WEMA) project, which has developed and disseminated drought-resistant maize varieties incorporating traits for improved WUE and insect resistance. As of October 2025, these and related TELA varieties have reached millions of smallholder farmers across sub-Saharan Africa, impacting up to 44 million people and resulting in yield improvements of 24-35% under drought stress compared to traditional maize, with some cases reporting up to 54% increases.[49][50][51][52]References
- https://www.[mdpi](/page/MDPI).com/2077-0472/10/9/370
